Dietary biology of the Eurasian eagle-owl
The Eurasian eagle-owl (Bubo bubo) may well be the most powerful extant species of owl, able to attack and kill large prey far beyond the capacities of most other living owls. However, the species is even more marked for its ability to live on more diverse prey than possibly any other comparably sized raptorial bird, which, given its considerable size, is almost fully restricted to eagles. This species can adapt to surprisingly small prey where it is the only kind available and to large prey where it is abundant. Eurasian eagle-owls feed most commonly on small mammals weighing 100 g (0.22 lb) or more, although nearly 45% of the prey species recorded have an average adult body mass of less than 100 g (3.5 oz). Usually 55-80% of the food of eagle-owls is mammalian.
Hunting and digestion
Hunting mainly consist of the owl watching from a perch for prey activity and then swooping down swiftly once prey is spotted. The prey is often killed quickly by the eagle owl's powerful grip and talons though is sometimes bitten on the head to be killed as well. Then the prey item is swallowed whole or torn into pieces with the bill. The same basic hunting and killing methods are used by all owls in the Bubo genus, except that the snowy owls (Bubo scandiacus) and fish owls regularly watch for prey from a ground position (on a bank in the case of fish owls). Most hunting occurs in wood-cloaked openings, often those carved out by wetlands or watersheds. While they can and do hunt within woodlands, they are not well suited to hunting in areas with dense understories, thick foliage or tree thickets, as they seem to hunt firstly by vision and only secondarily by sounds, unlike some other owls. Eurasian eagle-owls are too heavy with relatively modest wing areas to hunt extensively on the wing although this species’ relatively short, broad wings allow it low-speed maneuverability in the moments are it takes off after they spot a prey item. Because of the limits of its flying abilities, the Eurasian eagle-owl requires ample, elevated perches from which to watch for prey activity and thus in most areas it will not hunt extensively in open, treeless areas, unlike smaller owls like the barn owl (Tyto alba). Tree branches are often the main hunting perches used but they will also use rock formations, rubble with large rocks, hills with tall grasses or even a building, tall pole or other elevated manmade perch. Occasionally, they may capture other birds on the wing, including nocturnal migrants, taking advantage of their distraction and diminished visual acuity to intercept them in mid-flight. They seem to hunt mostly by opportunity, taking whatever detectable prey item that is available, preferably those that are active. Most prey, even up to the size of small rabbits, are swallowed whole. While a small rodent can easily be swallowed in an instant, if the prey item is large, the swallowing process can appear grueling and grotesque and in some cases eagle-owl nestlings have choked to death while attempting to swallow overly large prey (i.e. moorhens). Small prey is often swallowed immediately after capture, although occasionally it is carried in the bill to the nest for the young or to a roost for quick consumption. Larger prey is normally carried in the owl's feet and is more likely than smallish prey to be brought to the nest due to its nutritional value. Exceptionally large prey (probably any over 3,000 g (6.6 lb)) is consumed on the ground where it is killed, possibly being torn apart into manageable pieces. This leaves the owl vulnerable to loss of their prey to scavengers or to confrontations with heavier predators. The undigestable portions of prey are regurgitated in the form of pellets as in all owls. Pellets of the Eurasian eagle-owl average around 75 mm × 32 mm (3.0 in × 1.3 in), thus they are around the same size as those of most other large Bubo owls, even the notably smaller great horned owl (B. virginianus). In some cases, pellets of Bubo owls can range up to 150 mm (5.9 in) in length. Eagle-owl pellets average slightly larger (about 10%) than those of great grey owls (Strix nebulosa). As is the case with all owls, pellets are indisputably the best method to examine the main diversity of prey consumed by an owl. However, it is also important to examine the prey remains left around a roost or nest when available. Larger prey, which may be torn apart before the eating of portions or fleshy parts of the prey item, is frequently determined solely by remains rather pellets as are birds, in which the wings, feet and some feathers may be removed before consumption. As in the great horned owl, after capturing larger prey, the Eurasian eagle-owl often beheads it. In part, this may be due to making prey easier to carry off and, in both large owl species, it is considered a signature indicator for predator identification.
Summary of general diet
The diet is generally more diverse than any other co-existing owl but often focuses predominantly on a particular range of prey species, with two to four species often making up the majority of the diet. Studies conducted over the course of years has shown that the regional diet often changes dramatically from year to year. This is partially driven by the cyclical population trends of much of their prey as well as by habitat changes, which are often due to human activities. The primary prey species varies by region but is comprised mainly by small mammals such as voles, rats, mice, rabbits and hares. In Europe, the five main prey species are, in order of extent of reporting and numeric abundance in dietary studies: the brown rat (Rattus norvegius), which has now occupied edge habitats (although generally associated with man) in almost every part of Europe excluding the colder north; the common vole (Microtus arvalis), often the most abundant native, small mammal in wild portions of Europe; the European hedgehog (Erinaceus concolor), which occupies wooded edges across western Europe alongside the eagle-owls; the European water vole (Arvicola amphibius), a unique, large vole occupying the wetland edges often hunted by eagle-owls; and the European rabbit (Oryctolagus cuniculus), which has a very close relationship with the eagle-owls found throughout the Iberian Peninsula and the massifs of France. As the distribution of the Eurasian eagle-owls moves west (and south), the primarily prey species gradually change but often continues to be dominated in number by small rodents and in biomass by slightly larger mammals such as hedgehogs and hares and rabbits.
A very large balance of the prey range can also be comprised by birds and other prey including reptiles, amphibians, fish, insects and other invertebrates are seemingly taken whenever they are available. All told, well more than 600 different species have been identified as prey of Eurasian eagle-owls. Their diet includes basically all the same prey as all sympatric diurnal raptors in the genera Buteo, Aquila and Haliaeetus. The total number of prey species may even surpass that of the great horned owl and may well be the greatest of any raptorial bird on the Eurasian continent. Among five segments of Europe the average prey diversity per region was 63 species, a higher number than any of the other 40 raptorial bird species studied there. The mean mass of prey per study has varied from as little as 84.2 g (2.97 oz), near the now former Aral Sea in Turkmenistan with the Turkmen jerboa (Jaculus turkmenicus) being the primary prey species, to 1,037.9 g (2.288 lb), in Spain with the European rabbit being the primary prey species. Remarkably, in northern Spain, where the rabbit is now extirpated (as was the eagle-owl for a time in the 20th century), the average weight of prey can dip as low as 87 g (3.1 oz). In comparison, the lightest mean prey mass in dietary studies of the great horned owl was 22.5 g (0.79 oz) while the highest was 610.4 g (1.346 lb).
Most dietary studies place the average weight of Eurasian eagle-owl prey in the zone of 100 to 500 g (0.22 to 1.10 lb), thus the species fits well within the rule of thumb that most prey weigh no more than 20% of the raptorial bird's own weight. It should be noted that the average prey weight in comparison to the eagle-owl's body mass is reportedly average and unremarkable for both owls and raptors in general, the average prey per one study was 7.2% of the eagle-owls’ body mass. The European raptorial birds most likely to attack prey of a relatively large size compared to themselves were the black kite (Milvus migrans), whose average prey was 35.7% of its own weight, and the Eurasian pygmy owl (Glaucidium passerinum), whose average prey was 31.7% of its own weight. On the other hand, when rabbit numbers were at their peak, the average prey mass in Spain may range up to at least 55% of the eagle-owls’ own body mass in that population. A raptorial prey comparison estimated that the mean prey weight for eagle-owls in Europe was 294.7 g (10.40 oz) as a mean among 5 main regions, the highest of any owl but similar or slightly lighter than the European average for northern goshawks (Accipiter gentilis) and considerably lower only than two widespread European eagles. Per that study the average prey weight of the great horned owl in 4 North American regions was much lower (averaging only 64 g (2.3 oz)). In Mediterranean scrub, the average mammalian prey of the Eurasian eagle-owl was nearly five times heavier than those of great horned owls from similar habitats in Chile, California and Colorado, where in combination the horned owl's mammalian food averaged 230 g (8.1 oz). However, a comparison between eagle- and horned owls based upon six comparable biomes in the Americas and Eurasia found the great horned owl's prey averaged 372 g (13.1 oz), improbably slightly higher than the eagle-owl at 327 g (11.5 oz). If known Asian studies are mixed with European ones, the average prey weight for the Eurasian eagle-owl overall may also roughly be 372 g (13.1 oz). Among sympatric owls in Europe, the mean prey weight of long-eared owls (Asio otus) was found to be 32 g (1.1 oz), the tawny owl (Strix aluco) took prey weighing a mean of 34.5 g (1.22 oz) (though locally can be as high as 130 g (4.6 oz)) and short-eared owls (Asio flammeus) mean prey weigh was 35 g (1.2 oz). A study in Finland seeking to distinguish the differences in prey taken by females and smaller male eagle-owls found that the two sexes prey averaged 828 g (1.825 lb) and 575 g (1.268 lb), respectively. The species taken as food by the two sexes there were largely the same but the female simply often caught the larger prey individuals.
In terms of sheer quantitative abundance, rodents are by far the most dominant prey group in the diet of the Eurasian eagle-owl. Roughly 130 species of rodent are known to have been taken by these owls. Due to their small sizes, however, rodent prey often comprise a relatively small portion of the prey biomass, excepting relatively large rodents such as rats and hamsters, some of which weigh at least 300 g (11 oz). In many parts of Europe, the most numerous prey in dietary studies are the 360 g (13 oz) brown rat and the 28.5 g (1.01 oz) common vole, followed by the nearly as widespread 40 g (1.4 oz) field vole (Microtus agrestis). Among the areas where the common vole was the leading prey species included southern Sweden, Germany, Poland, the Czech Republic, and Slovakia. In areas that have undergone more heavy development, the brown rat predominates, being the leading prey item in several parts of France including Côte-d'Or, Lozère and even the remote Pyrenees, Belgium, the Italian Alps, and Brașov, Romania. The brown rat is even the primary prey in Lebanon despite it being tied solely to human habitations as the environment is often too arid to allow it to survive further afield. Black rats (Rattus rattus), at 200 g (7.1 oz), are also hunted but rarely in equal number to the generally more successful brown rats. In Norway and Finland, field voles were the most numerous prey species, per one study in the latter country it made up 30.1% of the food but only provided 3.3% of the prey biomass. The European water vole, averaging at 75 to 140 g (2.6 to 4.9 oz), was the main prey species in Styria, Austria, although considerably secondary in biomass to hedgehogs, as well as in central Sweden. The water vole often the second or third most regularly found prey species in several other European studies. In Samara, Russia, the diet is dominated by the European water vole, although other species such as European hamsters (Cricetus cricetus) and European hares (Lepus europaeus) (both also significant prey there) probably outweigh them in biomass contribution. The common vole and European water vole together made up roughly 80% of the prey by number in the High Tatras of Slovenia and more than 60% of the diet in bordering Poland.
In the northern extremes of their range, Eurasian eagle-owls tend to have a less varied diet than those to the south and the need to catch significant numbers of rodents rises as they are often the only regularly accessible prey in sparse sub-Arctic environments. In northern Sweden, more than 60% of the food was made up of microtine rodents, i.e. the 70 g (2.5 oz) Norway lemming (Lemmus lemmus), the field vole, the European water vole and the 36 g (1.3 oz) grey red-backed vole (Myodes rufocanus). In one study from western Russia, rodents comprised more than 90% of the diet of the eagle-owls, led by the 25 g (0.88 oz) steppe lemming (Lagurus lagurus) at 24% by number, the 27 g (0.95 oz) narrow-headed vole (Microtus gregalis) at 21% and the European water vole at 17.9%. Similarly in high altitude tundra of the East Austrian Alps, nearly 90% of the food was found to be comprised by microtine rodents, the 54 g (1.9 oz) European snow vole (Chionomys nivalis) being the most frequently identified species in the diet. In Spain, the 19 g (0.67 oz) Algerian mouse (Mus spretus), at up to 41.8% of the prey by number, and 24 g (0.85 oz) wood mouse (Apodemus sylvaticus), at up to 10.5% by number, are often regularly taken, especially in regions where rabbit numbers have declined. In Romania, the 98 g (3.5 oz) Romanian hamster (Mesocricetus newtoni) and 365 g (12.9 oz) European hamster are the most prominent species found in the eagle-owl's diet, alongside the brown rat. The Romanian hamster is also dominated the prey list per a study in Bulgaria, only the European water vole follows distantly in number. Dormice are readily taken when available in Europe, especially the 127 g (4.5 oz) edible dormouse from central Europe to the eastern countries. In Slovenia, the edible dormouse was the most regularly-recorded prey species, making up 20.2% of the food but it comprised 9.4% of the biomass. The edible dormouse was also the most regular prey species in Trentino-Alto Adige/Südtirol, Italy, making up 22.5% of the diet. The smaller 82.5 g (2.91 oz) garden dormouse (Eliomys quercinus) and considerably smaller 27.3 g (0.96 oz) hazel dormouse (Muscardinus avellanarius) are also occasionally predated in Europe, plus at least a half dozen other dormouse species in eastern Europe, Asia Minor and several points to the east.
Jirds, jerboas, gerbils and hamsters, particular the genera Allactaga, Ellobius, Gerbillus, Meriones, and Pygeretmus, start to become noticeable in the diet in the more arid portions of this species’ range, i.e. from Asia Minor to the Middle East and Central Asia. Relatively large species such as 100 g (3.5 oz) Tristram's jird (Meriones tristrami) and the 162 g (5.7 oz) Euphrates jerboa (Allactaga euphratica) are often amongst the more prominent species to be hunted. In western Kazakhstan, the primary foods are the 350 g (12 oz) great jerboa (Allactaga major) and 55 g (1.9 oz) northern mole vole (Ellobius talpinus) while on the Buzachi and Mangyshlak Peninsulas of the Kazakh Caspian Sea, the primary foods were the 100 g (3.5 oz) Libyan jird (Meriones libycus), 285 g (10.1 oz) great gerbil (Rhombomys opimus) and 58.7 g (2.07 oz) small five-toed jerboa (Allactaga elater). All told, in the peninsular Kazakh regions of the Caspian Sea, jirds, jerboas and gerbils made up about 92% of the food. In the Tibetan Plateau of China, the 54 g (1.9 oz) tundra vole (Microtus oeconomus) is the leading prey species, making up 53.1% of the prey. In Mongolia, two rather small rodents, the 24 g (0.85 oz) Mongolian five-toed jerboa (Allactaga sibirica), at 23.6% of the prey, and the 17 g (0.60 oz) Campbell's dwarf hamster (Phodopus campbelli), at 14.5% of the prey, make up a majority of the prey by number. In the Transbaikal, the 24 g (0.85 oz) Chinese striped hamster (Cricetulus barabensis) was the main prey species, making up 43.8% of the diet.
What all primary rodent prey species share is that they are either nocturnal or crepuscular and are often common to abundant in openings of woods and rocky environments. The reason Eurasian eagle-owls take rats, which associate rather closely with humans, much more regularly than they take house mice (Mus musculus) is not their larger size (many other rodents regularly taken by eagle-owls are as small or smaller than a house mouse) but the rat's ability to flourish along the edges of crop fields, refuse dumps, roadsides and abandoned buildings and fields, whereas the mice are more closely tied to active human habitations. A single refuse dump can host several thousand rats and eagle-owl territories that include dumps can locally expect higher productivity due to the abundance of this food source. Squirrels are readily predated but, being diurnal, are largely unavailable to this and other owls. When they are captured, it is presumably around dawn or dusk from their tree hole, in species such as the widespread 315 g (11.1 oz) red squirrel (Sciurus vulgaris), or burrow entrance, in the case of ground squirrels, most regularly recorded as prey in Asia Minor and the Central Asia. A few specimens of the 2,000 g (4.4 lb) woolly flying squirrels (Eupetaurus cinereus), the largest of the world's flying squirrels and one of the rarest, were the only identified foods for Eurasian eagle-owls in northern Pakistan alongside some European hares. Although not common in the diet, a few species of marmot have been taken and may be an important aspect of the prey biomass. In Europe, adult-sized alpine marmots, (Marmota marmota) have been killed. However, the average weight of Tarbagan marmots (Marmota sibirica) taken in Mongolia was only 1,500 g (3.3 lb) and that of alpine marmots in Engadin, Switzerland was only 2,000 g (4.4 lb). These obviously comprising young marmots as adults have average weights from 3,500 to 7,000 g (7.7 to 15.4 lb), from spring low weights to pre-hibernation weights during autumn hypophagia. Other than marmots, the largest rodent known to be hunted by Eurasian eagle-owls is the introduced aquatic rodents, the muskrat (Ondatra zibethica), which in one study estimated to average 1,300 g (2.9 lb) when taken, and the nutria (Myocastor coypus), equal in size to the large marmots.
Throughout the western Mediterranean region, the Eurasian Eagle-Owl is something of a specialist on a single prey species: the European rabbit. The rabbit historically reached extremely high densities in Iberian scrub, i.e. more than 40 per every 1 square hectare (2471 square acres). In central Spain, up to 73.1% of the prey that were recorded for Eurasian eagle-owls, by number, can be rabbits. Where still available, they are also the main prey in Portugal and central France. However, following the devastation of the wild rabbit due to rabbit haemorrhagic disease, the local eagle-owls have frequently had to adapt to other, often smaller, prey. On the other hand, given the now much reduced numbers of rabbits, the eagle-owls still regularly select rabbits, seemingly out of proportion to their commonality. Although large mature wild rabbits commonly weigh 1,700 to 2,400 g (3.7 to 5.3 lb), the eagle-owls usually hunt smaller specimens, often with an average weight around 1,000 g (2.2 lb), with young rabbits usually selected in spring and summer and subadults selected in the autumn and winter. This is largely due to the behaviour of rabbits, with younger rabbits being forced to distribute following weaning, being less cautious in behaviour and occupying less primary habitat, thus being forced out of the confines of their burrows more regularly than mature adults. However, the estimated average weight of rabbits taken can be variable, reported from as little as 800 g (1.8 lb) in a study from Spain to as much as 1,900 g (4.2 lb) in the Netherlands.
Three other lagomorphs extensively overlap in range with Eurasian eagle-owls in Europe, the mountain hare (Lepus timidus) in the northern portions, the European hare (Lepus europaeus) in the central and eastern portions and the Granada hare (Lepus granatensis) in the western Mediterranean portions. These species are all larger on average than a rabbit, averaging 2,000 g (4.4 lb) in the Granada hare, roughly twice that in the European hare and the mountain hare being intermediate between the two. Hares are often considerably secondary in prey remains in most European biomes by number but often are a significant contributor of prey biomass for eagle-owls. For example, in Finland, the mountain hare made up only 5.3% of prey by number but made up 56.2% of the prey biomass as the hare specimens were all large, with an estimated mean mass of 3,900 g (8.6 lb). On the contrary, the mountain hare was the numerous prey species in one study from the Swiss Alps, making up 28.3% of the prey by number. Another area near Europe where hares were numerically important was in southwestern Turkey, with the European hare being the second most common prey species by number. There it consisted of 18.1% of the quantity and presumably a huge portion of the biomass. In lower Austria, the European hare was also the second most abundant species in the diet but the estimated average weight of hares taken was rather low, at 850 g (1.87 lb), indicating young hares of probably less than a month old are most often taken there. On the other hand, in Slovenia, Netherlands and Bavaria, the European hares taken were estimated to average 2,500 g (5.5 lb), 4,500 g (9.9 lb) and 4,750 g (10.47 lb), respectively. The European hare was also the second most common prey species in a study from the Czech Republic.
Outside of southwestern Europe, the next closest association between lagomorphs and this species is in the arid steppe of southern Russia, hares are apparently the primary prey of the local eagle-owls. Little has been published in recent ornithological review, but old studies have indicated that the eagle-owls in this region are so dependent on hares, primarily again the mountain hare species, that cyclical reductions in numbers of the hares are followed immediately by a reduction of the local eagle-owls. A similar phenomenon has been noted in the great horned owl in its association with the snowshoe hare in the American boreal forest. The same prey, the mountain hare, was the most important along the Pechora River in Russia, making up 34.1% of prey numbers, although the general habitat is distinctly different from the steppe, as it consists of mountainous sub-taiga dense forests. Together with sizeable numbers of Eurasian red squirrels and large forest grouse which are the next most significant prey types by number, the mean prey size along the Pechora is presumably extremely large. Although in surrounding arid lowlands the food is almost totally dominated by gerbils, jirds and their kin, in the Pamir Mountains of Tajikistan and Afghanistan, the cape hare (Lepus capensis) was the leading prey species, making up 44% of the prey numbers. In Mongolia, tolai hare (Lepus tolai), of similar size to the cape and Granada hare, were the most significant contributor of prey biomass, making up 30.6% of biomass but only contributed 4% of the prey by number Other than the prior mentioned species, at least five other species of hare have been found as occasional contributors to the eagle-owl's diet. The only other family in the lagomorph order, the pikas, have been found to factor regularly into the diet of Eurasian eagle-owls as well, mainly in the mountainous regions of Asia. Pikas are much smaller than rabbits and hares, averaging 70 to 185 g (2.5 to 6.5 oz) amongst the know prey species. One study in Mongolia found that Daurian pikas (Ochotona dauurica) made up 73% by number of the remains. In the Tibetan Plateau, the plateau pika (Ochotona curzoniae) and gansu pika (Ochotona cansus) were the second and third most numerous prey species. The more sizeable large-eared pika (Ochotona macrotis) was the second most regular prey species in the Pamir Mountains, comprising 10.8% of the remains.
Hedgehogs often comprise a fairly significant portion of the prey taken by Eurasian eagle-owls, both in numbers and biomass. At least eight species of hedgehog have been predated. The European hedgehog is often one of the most prominent prey species in eagle-owl diet studies from Europe, and was recorded as the most numerous prey species per researchers in parts of Denmark, Switzerland, Austria and south Germany. With an average weight of 500 to 1,000 g (1.1 to 2.2 lb), the European hedgehog can comprise a very large portion of the biomass. A study of the Bavarian region of Germany, the European hedgehog (the main prey species) made up 41.7% of the prey by number and 52.1% of the biomass, the maximum representation of hedgehogs known in Europe. Other members of the Erinaceus genus are also locally regularly taken, as is the 575 g (1.268 lb) Daurian hedgehog (Mesechinus dauuricus) in Mongolia. Studies from Greece and the Czech Republic found that the northern white-breasted hedgehog (Erinaceus roumanicus) was the leading prey species. Unidentified Erinaceus hedgehogs almost totally dominated the diet of eagle-owls in Stavropol, Russia, making up 70.9% of the food, only the European rabbit has been found as more significant at the genera level by number in a given dietary study. Studies from both Syria and Kazakhstan showed that the 365 g (12.9 oz) long-eared hedgehog (Hemiechinus auritus) was the most significant prey, making up 25.3% and 33.6% of the prey remains, respectively. After killing hedgehogs, the Eurasian eagle-owls peel the prickly skin off their backs before consumption, frequently resulting in up to dozens of hedgehog backs being found around nests. Moles and shrews are readily hunted but are usually only a secondary portion of the diet. Eurasian eagle-owls have been recorded hunting the smallest mammal on earth (by weight) the 1.8 g (0.063 oz) Etruscan shrew (Suncus etruscus), as well as the largest mole on earth, the 440 g (16 oz) Russian desman (Desmana moschata). From the smallest shrew to the heaviest hedgehog, the Eurasian eagle-owl has been verified to hunt the full size range of insectivores. They've also attacked bats of every size available, from the smallest European bat, the 5.7 g (0.20 oz) common pipistrelle (Pipistrellus pipistrellus), to the largest species there, the 59 g (2.1 oz) greater noctule bat (Nyctalus lasiopterus). In the Sikhote-Alin range of the Russian Far East, bats were found to comprise 5.9% of the remains and, of five local owl species, the Eurasian eagle-owl was the most regular predator of bats in the area.
Larger and more dangerous mammalian prey is not infrequently tackled by Eurasian eagle-owl. Nearly thirty species of mammalian carnivores have been reported in their diet. Many of these are mustelids, which are the smallest type of carnivore but can defend themselves viciously, even the tiny 67 g (2.4 oz) least weasel (Mustela nivalis). Nonetheless, unlike some smaller birds of prey, the Eurasian eagle-owl seems to have no problem subduing various weasels and even martens, some of the latter can nearly equal to their own weight, and will kill the young of much larger species such as European otter (Lutra lutra) and Eurasian badger (Meles meles). However, the single most widely reported carnivore is the red fox (Vulpes vulpes), as they've been recorded in the diet from Denmark and Spain to the Russian Far East. Many fox specimens taken by eagle-owls are young individuals or subadults. Some studies posited that the average fox taken as weighing about 2,500 to 3,000 g (5.5 to 6.6 lb), about equal to the eagle-owl's own weight, but another noted fox specimens killed that were estimated to weigh 8,000 g (18 lb), much larger than the eagle-owls. At least four other species of foxes have been verified as prey in the Middle East and Asia. Raccoon dogs (Nyctereutes procyonoides), averaging 6,500 g (14.3 lb), have been preyed on in Asia as well. Other relatively large carnivores have been hunted as well, including invasive Egyptian mongoose (Herpestes ichneumon) in Spain and masked palm civets (Paguma larvata) in China, both being roughly cat-sized at averages of 2,300 and 4,300 g (5.1 and 9.5 lb), respectively. Domestic carnivores including cats (Felis silvestris catus) of all sizes and small dogs (Canis lupus familiaris) or puppies may on occasion become prey for Eurasian eagle-owls. Cats killed have been estimated to weigh from 3,200 to 7,500 g (7.1 to 16.5 lb). The dogs killed by Bavarian eagle-owls were estimated to average 4,000 g (8.8 lb). Non-native carnivores such as American mink (Neovison vison) and raccoon (Procyon lotor) have also been preyed on by eagle-owls, which is presumed to incidentally benefit the prey taken in considerably numbers by these rarely checked invasive fur-bearers.
The Eurasian eagle-owl is perhaps the only living owl widely reported (if not commonly) to kill the young of ungulates. At least nine species have been identified as their food. It is possible that some ungulates are eaten as carrion but this species, like most owls, normally kills its own food, unlike many eagles many of which consume carrion regularly. Among the ungulate prey recorded are three species of deer and five species of goat-antelopes, in addition to piglets of wild boar (Sus scrofa). Only the weight of the roe deer (Capreolus capreolus) has been widely approximated when taken and specimens killed have included: a 10,000 g (22 lb) deer, a 13,000 g (29 lb) specimen and even, in the small adult size range for this deer, 17,000 g (37 lb), all considerably larger than the eagle-owls themselves and far larger than any prey known for other owls. In studies from Bavaria and Austria, the average weight of roe deer caught was only 1,500 and 2,500 g (3.3 and 5.5 lb), indicating very young deer being typically taken. Even if taken as newborn kids, fawns or calves, the young of other ungulates taken would weigh at least 2,500 to 7,000 g (5.5 to 15.4 lb), from the birth weight of ibex (Capra ibex) to that of red deer (Cervus elaphus). Perhaps even larger, the rare domestic sheep (Ovis aries) taken by eagle-owls can reportedly include “half-grown” individuals.
The Eurasian eagle-owl may hunt at least 300 species of bird. In Europe, the most common avian prey species are the normally feral or domestic 355 g (12.5 oz) rock pigeons (Columba livia), although the 490 g (17 oz) common wood pigeon (Columba palumbus) can be locally even more significant. In the Netherlands, the common wood pigeon is the most important prey species, making up 37.3% by number and 38.3% by biomass. Yet another, smaller study of the Netherlands found the rock pigeon to be the primary prey species. In a dietary study from Luxembourg, the common wood pigeon was the most frequent prey species, making 19% of the remains by number. A study from Romania listed the rock pigeon was the second most frequently recorded prey behind only the Romanian hamster and the largest contributed of biomass. Unusually, in the Netherlands, birds were the primary food in both number (77.6%) and biomass (72%). Also, in Luxembourg, eagle-owls hunted birds in general were more regularly than mammals, as nearly 70% of prey remains there were avian. At least six other species of pigeon and dove have also been recorded as prey. However, perhaps the most significant contributor of prey at the family level is the corvids and all available species have been targeted. The 570 g (1.26 lb) carrion crow (Corvus corone) is the second most widely recorded avian prey species in Europe and, locally, good numbers are also taken of 490 g (1.08 lb) hooded crow (Corvus cornix), 245 g (8.6 oz) western jackdaws (Corvus monedula), 160 g (5.6 oz) Eurasian jays (Garrulus glandarius), 1,085 g (2.392 lb) common ravens (Corvus corax), 455 g (1.003 lb) rooks (Corvus corone), two species each of magpie and chough and the 183 g (6.5 oz) spotted nutcracker (Nucifraga caryocatactes), in rough descending order of reportage in the eagle-owl's diet. In Baden-Württemberg, Germany, the carrion crow was the most frequently recorded bird among an exceptionally diverse recorded prey base including than 65 bird species there (although birds only comprised 27% of the prey numbers overall). Unlike smaller passerines, corvids roost in numbers in relatively open spots, which make them fairly vulnerable to a predator as stealthy and powerful as the eagle-owl. More than 17 species of gamebirds have been recorded in the Eurasian eagle-owl's diet but they are normally taken in small numbers. There are, however, exceptions. In one study conducted in lower Austria, the most frequently identified prey species was the 405 g (14.3 oz) grey partridge (Perdix perdix), which is the most widely reported gamebird prey for eagle-owls in Europe. One study of a “primeval” forested region of Finland found various grouse species to be the most significant contributor of biomass, namely in descending order the 2,950 g (6.50 lb) western capercaillie (Tetrao urogallus), the 1,080 g (2.38 lb) black grouse (Tetrao tetrix) and the 429 g (15.1 oz) hazel grouse (Bonasa bonasia). In inland areas of Norway, the large forest grouse were also significant biomass contributors. The same forest grouse species were also found to be significant to diet along the Pechora River in Russia. Other gamebirds can be important secondary prey species in different parts of Europe: the 528 g (1.164 lb) red-legged partridge (Alectoris rufa) in western Europe, the 615 g (1.356 lb) rock partridge (Alectoris graeca) and the 535 g (1.179 lb) rock ptarmigan (Lagopus mutus) in alpine highlands, the 1,135 g (2.502 lb) ring-necked pheasant (Phasianus colchicus) in eastern Europe and the 570 g (1.26 lb) willow ptarmigan (Lagopus lagopus) in the sub-Arctic zone. In Turkey, the most significant prey by number was the 503 g (1.109 lb) chukar (Alectoris chukar), comprising 20.5% of remains. A Korean study in two habitat types (forest and field) found that ring-necked pheasants were the main prey species, making up an average of 19.33% by number and 34.81% by biomass. Other birds of prey are perhaps second only to pigeons and corvids amongst avian contributors to the diet (their ecological relationships with eagle-owls are explored in more detail below).
Among coastal and some wetland areas, various water birds can come to contribute a large portion of both prey numbers and prey biomass. This may include more than 50 species of shorebird (from the one of the smallest sandpipers to the largest species of gull), more than 30 species of waterfowl, more than 10 species of herons, more than 8 species of rails and any grebes, cormorants or other water birds that are available. The most regularly reported water bird prey in Europe were, roughly in this order, the 343 g (12.1 oz) common moorhens (Gallinula chloropus), the 836 g (1.843 lb) Eurasian coot (Fulica atra), 1,140 g (2.51 lb) mallards (Anas platyrhynchos), 284 g (10.0 oz) black-headed gull (Chroicocephalus ridibundus), and the 340 g (12 oz) Eurasian teal (Anas crecca). The diet of a handful of eagle-owl pairs in the Riau Islands Province of France were found to be dominated by water birds, especially the 1,154 g (2.544 lb) yellow-legged gull (Larus michahellis), the colonial abundance of which allowed the eagle-owls to atypically occupy these small islands. The diet of eagle-owls in Norway was dominated in coastal areas by water birds, overall for the nation 53% of the food was made of birds, the species most commonly identified as caught being the 388 g (13.7 oz) mew gull (Larus canus), 430 g (15 oz) common puffin (Fratercula arctica) and 2,070 g (4.56 lb) common eider (Somateria mollissima). Despite access to large seabird breeding colonies, almost all large bird species hunted in Norway, including large forest grouse in more inland areas, were apparently fully-grown adults and most water birds were caught while resting on open coastal waters. Eagle-owls in northwestern Poland, an area heavily dotted with lakes, relied on birds for about 64% of the diet, more than half of which were water birds. The main prey species there was the Eurasian coot, at nearly 15% of the prey numbers. In Primorsky Krai in Russia, 53.2% of the food for the eagle-owls were made up of birds, predominantly water birds with the primary prey species being the 260 g (9.2 oz) crested auklet (Aethia cristatella ) (26.9%). In the Russian Far East, similarly, birds occupy up to 57.6% of the diet, a lion's share of which are water birds. In this study, the grey red-backed vole and reed vole (Microtus fortis) were the most numerous identified individual species but in some years the extremely large Japanese cormorant (Phalacrocorax capillatus), at 2,820 g (6.22 lb), were more numerous as prey than either vole. Water birds were found to be even more important in the diet in Korea, as in wetland habitat, with birds in general comprising 68.9% by number and 85.3% by biomass there, but in adjacent upland areas birds were slightly secondary to mammals, which made up 38.7% by number and 64.7% by biomass, led by the brown rat. In Korea, the mallard and the similar spot-billed duck (Anas poecilorhyncha) made up 38.1% of the biomass. Other recorded bird species in the Eurasian eagle-owl's diet includes all type of birds found in their range, including bustards, sandgrouse, parrots, cuckoos, swifts, the 67 g (2.4 oz) hoopoe (Upupa epops), the 56.5 g (1.99 oz) European bee-eater (Merops apiaster), the 31 g (1.1 oz) common kingfisher (Alcedo atthis), the 146 g (5.1 oz) European roller (Coracias garrulus), at least seven species of woodpecker (from the smallest to the largest European species) and more than 80 species of passerine. Among passerines, the only family reported widely as prey besides corvids are thrushes. In the Italian Alps, Turdus species were the fourth most frequently recorded type of prey. In particular, the abundant 103 g (3.6 oz) Eurasian blackbird (Turdus merula) is widely reported to be taken by eagle-owls. As thrushes are relatively small, at 55 to 130 g (1.9 to 4.6 oz) among the species known to be predated, pairs in the Italian Alps who depended more so on thrushes usually showed lower productivity during nesting attempts.
Wild birds found in their diet have ranged in size from the 9.5 g (0.34 oz) Eurasian wren (Troglodytes troglodytes) to about 15 species weighing over 2,000 g (4.4 lb). One of the largest wild adult bird verified as prey was the 3,300 g (7.3 lb) greylag goose (Anser anser). Other large species have been hunted, some may be cases of nest robbery rather than large adults but none are heavier than the largest mammalian prey that eagle-owls have taken including greater white-fronted goose (Anser albifrons), bar-headed goose (Anser indicus), great cormorant (Phalacrocorax carbo), Himalayan snowcock (Tetraogallus himalayensis) and demoiselle crane (Anthropoides virgo), all averaging around 2,500 g (5.5 lb), the 3,500 g (7.7 lb) swan goose (Anser cygnoides), the 5,500 g (12.1 lb) common crane (Grus grus) and the 8,000 g (18 lb) (between the dimorphic sexes) great bustard (Otis tarda). Eurasian eagle-owls have also hunted adult male western capercaillie, which average about 4,100 g (9.0 lb), although usually the much smaller females, at 1,800 g (4.0 lb), are more regularly taken. Although they rarely take domestic birds, the range of sizes killed is just as dramatic, from loose budgerigars (Melopsittacus undulatus), weighing only 29 g (1.0 oz), to domestic turkeys, which may easily weigh over 8 kg (18 lb).
Reptiles and amphibians are only an occasionally contributor to the diet in many regions. Most of the 30 or so species recorded have been taken as supplemental prey in Spain, i.e. several lizards (including geckos), frogs and toads, snakes and, to a lesser degree, turtles. One species widely and commonly reported in Europe outside of the Iberian region is the 23 g (0.81 oz) common frog (Rana temporaria). It was the leading prey, making up 45% of the prey found at nests in Rogaland, Norway. Also, the common frog was the second most abundant prey species in studies from southern Sweden, Valais and Engadin in Switzerland, Verbano-Cusi-Ossola, Italy and an enormous study from Slovakia, in the latter 10,476 frogs recorded making up 28.2% of the prey. There are no records of vicious fights between snakes and Eurasian eagle-owls as there are with the great horned owl, with the horned owl sometimes losing its life after attacking a snake. Perhaps with their larger size and greater power, the eagle-owl can more easily overpower any snakes they encounter, although most snakes in Europe and temperate Asia are not particularly large. Like the golden eagle, the eagle-owl may attack spur-thighed tortoises (Testudo graeca). In Lebanon, a “large adult” tortoise, which would be at least as heavy as the eagle-owl itself, was among their food items, although how they handle and eat this large, hard-shelled prey is not clear. Eurasian eagle-owls also opportunistically prey on fish, although never in large numbers, as fish are likely to be taken incidentally while hunting for other prey such as water birds. This species is known to take a greater diversity of fish (more than 30 species verified) and is more widely reported to hunt them than the great horned owl. Most of the fish recorded are medium-sized, with at least 10 each of various kinds of carp or cod, but several species averaging more than 2,000 g (4.4 lb) in mature mass have been taken, including common barbell (Barbus barbus), common carp (Cyprinus carpio), northern pike (Esox lucius) and a few species of trout, even bigger marine predators like the anglerfish (Lophius piscatorius) and European conger (Conger conger). However, in many cases small, young specimens may be caught of these large fish species rather than full-grown adults. Several species of insect and invertebrate have been identified in eagle-owl pellets. In some cases, these may be undigested insects in the stomachs of birds eaten by the eagle-owl but Eurasian eagle-owls have been verified as actively hunting insects and aquatic invertebrates such as snails and crabs before. Especially diverse in the diet are ground-based beetles, at least 20 species have been identified mainly those in the Carabus (ground beetle) genus.
Interspecies predatory relationships
The Eurasian eagle-owl is a very formidable bird of prey but its diet broadly overlaps with other European owls. All species of owl in the Europe and northern Asia hunt rodents, as does the eagle-owl, and in many the very same microtine rodents such as voles and lemmings will be favored. Even the 58.5 g (2.06 oz) Eurasian pygmy owl (Glaucidium passerinum), at a whooping one-fortieth of the weight of an eagle-owl, will take much the same rodent prey as eagle-owls in adjacent habitats. The only European owls to favor non-rodent prey are the 92 g (3.2 oz) European scops owl (Otus scops) and 169 g (6.0 oz) little owl (Athene noctua), both of which most regularly consume invertebrates. However, little owls also take rodents and small mammals, especially in the winter months (while scops owl migrate to Africa for the winter). The European owls with the most similar diets to eagle-owls are 475 g (1.047 lb) tawny (Strix aluco) and 785 g (1.731 lb) Ural owls (Strix uralensis), although both are considerably smaller and less powerful and more specialized to hunt in wooded environments. These two Strix species are highly territorial and sedentary like the eagle-owl and capable of taking a broad range of prey, including good numbers of birds and larger prey such as rabbits (for the tawny owl) and hares (for the Ural owl) of up to at least twice their own weight. Studies have indicated that even while selected similar prey species as the eagle-owl, smaller owls including the long-eared, tawny and Ural owls select smaller individual prey items, being more likely to take small, juveniles rather than optimal, large adults as does the eagle-owl. Similar rodent prey is also often taken by many diurnal birds of prey, especially buzzards, harriers and small falcons. However, due its greater size and power than overlapping owls and smaller diurnal raptors, it generally takes more diverse and larger prey than most overlapping raptorial birds.
In the Iberian peninsula, the Eurasian eagle-owl is part of a complex guild of predators that have evolved to survive mostly on European rabbits. Among this guild, golden eagles (Aquila chrysaetos) were recorded per one study to rely on rabbits for 40% of the diet, the eagle-owl for 49% of the diet, the Spanish imperial eagle (Aquila adalberti) for 50% of the diet, the Bonelli's eagle (Aquila fasciata) for 61% of the diet and the Iberian lynx (Lynx pardinus) for 79% of the diet. Elsewhere, the Spanish imperial eagle and eagle-owl are considered to outflank the golden and even the Bonelli's eagle as the most specialized avian predator of rabbits in the Iberian region. Other predators, such as common buzzard (Buteo buteo), northern goshawk (Accipiter gentilis) black kite (Milvus migrans) Iberian wildcat (Felis silvestris tartessia), red fox, stone marten (Martes foina) and introduced Egyptian mongoose also prey heavily on rabbits in Spain, but are more generalized and less reliant than the above predators. All these powerful predators do not generally compete directly for food but conflicts may ensue over the rights to territories and nesting sites amongst the birds. Being nocturnal in activity, however, the Eurasian eagle-owl does not tend to compete as directly as do the three eagle species and even these are discreetly segregated by habitat preferences, the goldens preferring open, steep cliffs, the Bonelli's favoring densely vegetated areas mixed with rocky spots and the imperial favoring relatively flat open woodlands. Among these eagles, the golden eagle tends to have the most similar habitat preferences to the Eurasian eagle-owl and across a broad band of overlapping distribution, the two are considered nearly ecological equivalents by day and night. However, good-sized female golden eagles are up to twice as heavy as an average eagle-owl, so seem to have a considerable advantage in size and power. Conversely, to support their large size and large territory needs, the golden eagle cannot survive on small and diverse prey nearly as successfully as the eagle-owl. Among the Iberian peninsula rabbit-eating guild, the species with wider ranges, the eagle-owl and the golden and Bonelli's eagles, have had some degree of success living off of alternate prey following the devastation of the rabbit population due to rabbit haemorrhagic disease. The two rabbit predators endemic to Iberia, the Iberian lynx and Spanish imperial eagle, have been devastated by the reduction and other causes and both are threatened species today.
Equally or even more so than the great horned owl, the Eurasian eagle-owl is a threat to any smaller type of raptor it encounters, whether other owls or diurnal birds of prey. All told, more than 20 species of accipitrid, 15 species of owl and 9 species of falcon have been found amongst their prey. The Eurasian eagle-owl is the primary predator of other birds of prey throughout Eurasia, not even the prolific raptor-killing northern goshawk (Accipiter gentilis) equals the sheer number of raptors taken. Up to 6% of the overall food by number and 36% by prey biomass for Eurasian eagle-owls can be comprised by other raptorial birds. The primary raptorial prey taken by Eurasian eagle-owls in Europe are two species: the 300 g (11 oz) long-eared owl and the 776 g (1.711 lb) common buzzard. Both are taken in such large numbers that they rank in the top five most regularly hunted bird species in Europe. In Luxembourg, the long-eared owl and common buzzard were the fourth and fifth most regularly hunted prey species. Other high rankings have included the long-eared owl being the fourth most regular prey species in Bavaria and the buzzard being the third most regular prey species in a study from the Czech Republic. While migrating, long-eared owls appear to select areas to move through partially based on whether or not eagle-owls are detected, thus eagle-owls have a very serious influence on the behaviour of this prey. Despite the large numbers taken of both of these, the more scarce eagle-owl does not seem to have a serious deleterious effect on their overall population, especially compared to anthropogenic factors.
Other than these two species, a large share of the raptorial prey for eagle-owls is made up of other owls. Given that all European owls are to some extent nocturnal, they may be encountered and killed upon detection by the Eurasian eagle-owl. In Europe, it has killed every other species of owl, from the tiny pygmy owl and scops owl to the large 1,078 g (2.377 lb) great grey owl and the 2,040 g (4.50 lb) snowy owl. The Eurasian eagle-owl is the only raptor that has been known to prey on snowy owl on multiple occasions. However, the threat Eurasian eagle-owls poses to other raptors can be exaggerated. Occasionally, with adequate mammal prey populations, they can nest as close as a few dozen meters of other raptors and never harass them. When nesting in the same groves as the 1,175 g (2.590 lb) long-legged buzzards (Buteo rufinus) in southeastern Bulgaria, Eurasian eagle-owls did not predate the buzzards at any point. Long-legged buzzards have been killed however in Kazakhstan. Even in those occasional cases where they pick off one or several raptors, they do not effect the overall population, unless the raptorial prey is already heavily diminished due to some other (often human-based) cause. For example, despite both being a known predator of both, they did not significantly depress numbers of either northern goshawks or tawny owls in southern Finland. One study showed that many raptors engage in spatial avoidance during potential encounters with Eurasian eagle-owls and while the predation by eagle-owls did decrease raptor population densities, they seldom caused declines in breeding success or altered habitat occupancy.
Discreet habitat preferences may coincidentally spare many owls, as owls from the genera Strix, Glaucidium, Aegolius and the 320 g (11 oz) northern hawk-owl (Surnia ulula) tend to restrict both nesting and their hunting forays to more enclosed areas of woodland than habitats inhabited by the eagle-owls. Meanwhile, Asio, Otus, Athene and barn owls owls tend to hunt in more open habitats than the edges favored by eagle-owls. However, habitat preferences are never enough to spare any of these genera from predation by the great eagle-owl. In the Italian Alps, despite differing habitat preferences and partially overlapping prey, several tawny owls were killed by eagle-owls. Woodland nesting owl species tend to nest in tree hollows, many of which are too small for an eagle-owl to access, so are somewhat less likely to be picked off at their nests. Open-country owls that tend to nest in open-access nesting sites like short-eared owls and little owls may be somewhat more vulnerable at the nest. The great numbers of long-eared owls taken, since it often nest in dense, protective thickets, are probably adult or immature owls attempting to hunt. In Europe, Eurasian eagle-owls are generally the only owls to regularly nest in rocky habitats. This is not the case in arid desert-like regions, where limited nesting options frequently force diverse owls to use rocky areas as nesting sites. However, the cliffs and other rocky areas preferred by Eurasian eagle-owls are also utilized by several species of diurnal raptor in Eurasia. In Spain, golden eagles, Bonelli's eagles and peregrine falcons (Falco peregrinus) most often nest on cliffs. Large scavenging birds such as cinereous vultures (Aegypius monachus), bearded vultures (Gypaetus barbatus), Eurasian griffons (Gyps fulvus), Egyptian vulture (Neophron percnopterus) and common ravens also often nests on the same Iberian cliffs. While the two eagles nested at great distances from one another (they are known to be territorial towards each other), the eagle-owl nesting within 2 to 3 km (1.2 to 1.9 mi) of the other species. In these cliff nests, the only considerable predatory interaction was the eagle-owls appearing to predate the peregrine falcons. In the Tibetan Plateau, upland buzzards (Buteo hemilasius) also seem to favor similar habitats and both the eagle-owl and buzzard take similar prey there. In general, the eagle-owl can nest closer to diurnal raptors because, as a nocturnal animal, it will not actively compete for territories as it would with other members of its own species.
While owls are apparently often killed by Eurasian eagle-owls while actively hunting, diurnal raptors are often ambushed at night at their large, conspicuous nests since they are easily located during hunting forays and the raptors are nearly defenseless in nocturnal conditions. The eagle-owl has been specified as the primary predator of common buzzards, peregrine falcons, common kestrel (Falco tinnunculus) and black kites. The common buzzard and 184 g (6.5 oz)common kestrel are probably the most often selected diurnal raptors because they inhabit the edges most often hunted by the eagle-owls. Studies have shown that 743 g (1.638 lb) peregrine falcon experience lower productivity in areas where they nest closely to eagle-owls, as the eagle-owls pick off both nestlings and adults by night. However, peregrine populations were not hugely effected except in cases where small reintroductions were attempted of falcons or falcon populations were already rare due to other causes. The northern goshawk is itself a serious predator of other raptors. The eagle-owl is the goshawk's only major predator, although goshawks are not as intensely hunted as are buzzards due to their more deeply wooded preferred nesting habitat.
Generally speaking, there appears to be rather strictly adhered size hierarchy among birds of prey and the very largest raptorial prey attacked by Eurasian eagle-owl tend to roughly equal to their own size. Larger raptors, such as eagles and vultures, seem to be largely invulnerable to eagle-owls. However, in Scandinavia, there are two cases of eagle-owls preying on “fairly large” nestlings of white-tailed eagles (Haliaeetus albicilla). Given the size, average adult weight of 4,780 g (10.54 lb), and formidable character of this eagle, it is possible that the young of other raptors larger than themselves may too be attacked. Eastern imperial eagles (Aquila heliaca), which are nearly as large as the white-tailed eagle at an average weight of 3,215 g (7.088 lb), have been killed by eagle-owls in Kazakhstan. Remarkable, considering the greater threat that the eagle normally poses to the eagle-owl than vica versa, it appeared a golden eagle was amongst the prey remains found around a nest in the French Pyrenees. Cases in Spain where large, formidable birds of prey, the Egyptian vulture (Neophron percnopterus) and Bonelli's eagle, that are roughly equal in size to the eagle-owls, both weighing just over 2,000 g (4.4 lb), have been predated, these seem to be taken from the nest or shortly after independence and rare occurrences. However, in Turkey, the eagle-owl is apparently a regular and serious predator of Bonelli's eagles. The Eurasian eagle-owl predates the largest members of the most species-rich diurnal raptor genera: the 900 g (2.0 lb) northern goshawks from the Accipiter genus, the 1,375 g (3.031 lb) upland buzzards from the Buteo genus and the 1,460 g (3.22 lb) gyrfalcons (F. rusticolus) of the Falco genus. Additional large raptors, i.e. those that can average 1,000 g (2.2 lb) or more in body mass, taken as prey include 1,485 g (3.274 lb) osprey (Pandion haliaetus), the 1,080 g (2.38 lb) red kites (Milvus milvus), 1,700 g (3.7 lb) short-toed eagles (Circaetus gallicus), the 2,205 g (4.861 lb) greater spotted eagle (Clanga clanga), the 1,370 g (3.02 lb) lesser spotted eagle (Clanga pomarina), and the rough-legged buzzards (Buteo lagopus) and saker falcons (Falco cherrug), in both of which females average more than 1,000 g (2.2 lb). The taking of rough-legged buzzards and snowy owls must be confined to full-grown victims, since they nest further north than Eurasian eagle-owls. Eurasian eagle-owls also hunt the smallest raptors available, including those such as lesser kestrels (Falco naumanni) and Japanese sparrowhawks (Accipiter gularis) that weigh less than 150 g (5.3 oz). Some of these are cases of eagle-owls killing nestlings or fledglings but they can easily overtake adult buzzards, goshawks and falcons of any size.
In rare cases, other predators may kill a Eurasian eagle-owl. In Europe, there is one case of a white-tailed eagle killing an eagle-owl and there are at least four known incidents of eagle-owls being killed by golden eagles. Also, an eagle-owl was found among the prey remains at a golden eagle eyrie in Mongolia. An eagle-owl was also found amongst the prey in the nest of steppe eagles (Aquila nipalensis) in Altai Krai, Russia. In 2016, a large female subadult Bonelli's eagle (Aquila fasciata) apparently preyed upon a three-year-old male Eurasian eagle-owl in Spain. Pine martens (Martes martes) and stone martens (Martes foina) are opportunistic nest predators. Although martens could probably reach most eagle-owl nests due to their agility and climbing abilities, they probably will attack nests when disturbance or low food supply result in lower nest attendance by the parent owls. Cases where nests have atypically been accessible on foot (for both humans and wild predators) have resulted in Eurasian eagle-owl nests being predated. Eurasian badgers, wild boars and raccoon dogs and raccoons, the latter two both where non-native in Germany, have also reportedly preyed on nests that they can access. In coastal areas of Spain, red foxes were reported to have preyed on four eagle-owls, including one unsexed brooding adult, at nests found to be reachable on foot by researchers. Cases of red foxes killing Eurasian eagle-owls at nests have reported elsewhere albeit very rarely, normally the eagle-owl is a greater danger to the foxes (and many of its other nest predators) than vice versa. In May 2017, a red fox was filmed killing two chicks and raiding the larder of an eagle-owl in Denmark.
- Schuchmann (1999). Eurasian Eagle Owl (Bubo bubo). pp. 186 in: del Hoyo, Elliott & Sargatal, eds (1999). Handbook of the Birds of the World. Vol. 5. Lynx Edicions, Barcelona. ISBN 84-87334-25-3
- Voous, K.H. 1988. Owls of the Northern Hemisphere. The MIT Press, 0262220350.
- König, Claus; Weick, Friedhelm (2008). Owls of the World (2nd ed.). London: Christopher Helm. ISBN 9781408108840.
- Jaksić, F. M., & Carothers, J. H. (1985). Ecological, morphological, and bioenergetic correlates of hunting mode in hawks and owls. Ornis Scandinavica, 165-172.
- Martínez, J. A., Serrano, D., & Zuberogoitia, I. (2003). Predictive models of habitat preferences for the Eurasian eagle owl Bubo bubo: a multiscale approach. Ecography, 26(1), 21-28.
- Martinez, J. A., Martinez, J. E., Manosa, S., Zuberogoitia, I., & Calvo, J. F. (2006). How to manage human-induced mortality in the Eagle Owl Bubo bubo. Bird Conservation International, 16(03), 265-278.
- Owls of the World: A Photographic Guide by Mikkola, H. Firefly Books (2012), ISBN 9781770851368
- Sergio, F. (2002). Biases associated with diet study methods in the Eurasian Eagle-Owl. J. Raptor Res, 36(1), 11-16.
- "Eurasian Eagle Owl - Bubo bubo - Information, Pictures, Sounds". Owlpages.com. 2005-04-21. Retrieved 6 March 2015.
- Cramp, S. 1985. Handbook of the birds of Europe, the Middle East and North Africa. Vol. 4. Oxford Univ. Press. Oxford.
- Laroulandie, V. (2002). Damage to pigeon long bones in pellets of the eagle owl Bubo bubo and food remains of peregrine falcon Falco peregrinus: zooarchaeological implications. In ZM Bochenski, Z. Bochenski, JR Stewart (Eds.), Proceedings of the 4th Meeting of the ICAZ Bird Working Group, Kraków, Poland, 11–15 September 2001. Acta Zoologica cracoviensia (Vol. 45, pp. 331-339).
- De Cupere, B., Thys, S., Van Neer, W., Ervynck, A., Corremans, M., & Waelkens, M. (2009). Eagle owl (Bubo bubo) pellets from Roman Sagalassos (SW Turkey): distinguishing the prey remains from nest and roost sites. International Journal of Osteoarchaeology, 19(1), 1-22.
- Lloveras, L., Moreno‐García, M., & Nadal, J. (2009). The eagle owl (Bubo bubo) as a leporid remains accumulator: taphonomic analysis of modern rabbit remains recovered from nests of this predator. International Journal of Osteoarchaeology, 19(5), 573-592.
- Willgohs, J. F. (1974). The eagle owl Bubo bubo (L.) in Norway; Part I- Food Ecology. Sterna, 13, 129-177.
- Hume, R. (1991). Owls of the world. Running Press, Philadelphia, PA. 1991.
- Delattre, P., Giraudoux, P., Baudry, J., Quéré, J. P., & Fichet, E. (1996). Effect of landscape structure on Common Vole (Microtus arvalis) distribution and abundance at several space scales. Landscape Ecology, 11(5), 279-288.
- Donázar, J. A., Hiraldo, F., Delibes, M., & Estrella, R. R. (1989). Comparative food habits of the Eagle Owl Bubo bubo and the Great Horned Owl Bubo virginianus in six Palearctic and Nearctic biomes. Ornis Scandinavica, 298-306.
- Jánossy, D., & Schmidt, E. (1970). Die Nahrung des Uhus (Bubo bubo). Regionale und erdzeitliche Änderungen. Bonner zool. Beitr, 21, 25-31.
- Marti, C. D., Korpimäki, E., & Jaksić, F. M. (1993). Trophic structure of raptor communities: a three-continent comparison and synthesis. In Current ornithology (pp. 47-137). Springer US.
- Jaksić, F. M., & Marti, C. D. (1984). Comparative food habits of Bubo owls in Mediterranean-type ecosystems. Condor, 288-296.
- Serrano, D. Interhabitat differences in the diet of the Eagle Owl (Bubo bubo) in the mid Ebro river valley (NE Spain): effect of European rabbit (Oryctolagus cuniculus) availability. Ardeola. Volume 45(1), 1998. Pages 35-46.
- Donázar, J. A., Travaini, A., Ceballos, O., Delibes, M., & Hiraldo, F. (1997). Food habits of the great horned owl in northwestern Argentine Patagonia: the role of introduced lagomorphs. Journal of Raptor Research, 31(4), 364-369.
- Simeonov, S., Milchev, B., & Boev, Z. (1998). Study of the Eagle Owl (Bubo bubo (L.))(Aves: Strigiformes) in the Strandzha mountain (Southeast Bulgaria). II. Food spectrum and trophic specialization. Acta zool. bulg, 50(2/3), 87-100.
- Olsen, Jerry. Australian high country owls. CSIRO PUBLISHING, 2011.
- Penteriani, V., Delgado, M. M. (2010) Búho real – Bubo bubo. En: Enciclopedia Virtual de los Vertebrados Españoles. Salvador, A., Bautista, L. M. (Eds.). Museo Nacional de Ciencias Naturales, Madrid.
- Mikkola, H., & Tornberg, R. (2014). Sex-specific diet analysis of the Eurasian Eagle Owl in Finland. Ornis Fennica, 91, 195-200.
- Geidel, C. (2012). Entwicklung neuartiger Schutzkonzepte für den Uhu (Bubo bubo) -Abschlussbericht 2012. Gutachten (DBU-Projekt).
- Schaefer, H. (1971). Beutetiere des uhus Bubo bubo aus Karpaten und Lappland. Bonner Zoologische Beiträge, 22, 153-160.
- Vondracek, J. (1983). Beitrag zur Nahrungsökologie und Nahrungszusammensetzung beim Uhu /Bubo bubo/ in den nordböhmischen Lokalitäten. Sylvia, 32: 39-54.
- Marchesi, L., Sergio, F., & Pedrini, P. (2002). Costs and benefits of breeding in human‐altered landscapes for the Eagle Owl Bubo bubo. Ibis, 144(4), E164-E177.
- Sandor, A. D., & Ionescu, D. T. (2009). Diet of the eagle owl (Bubo bubo) in Braşov, Romania. North-Western Journal of Zoology, 5(1), 170-178.
- Abel, J. LE GRAND-DUC D'EUROPE EN CÔTE-D'OR. CEOB- L’Aile Brisee/Tierecelet Infos: 54-62.
- Malafosse, J. (1985). Quelques données sur le Hibou grand-duc (Bubo bubo) dans le département de la Lozère de 1978 à 1984. Le Grand-Duc, 26, 26-32.
- Tavernier, G. "REGIME ALIMENTAIRE DANS LE TARN ET L'ARIEGE 2014". Hibou Grand-Duc en Midi-Pyrénées. Retrieved 6 March 2015.
- Balluet, P. (2011). Pathologie des proies du grand-duc. Le Grand-duc n°9/10 - LPO 2 Mission Rapaces.
- Bayle, P., & Prior, R. (2006). Prey species of Eagle Owl Bubo bubo in Lebanon. SANDGROUSE, 28(2), 167.
- Sackl, P., & Döltlmayer, G. (1996). Zur Siedlungsbiologie und Ökologie des Uhus Bubo bubo im oberen Murtal (Steiermark, Österreich) . Greife und Eulen Abh. Zool.-Bot. Ges. Österreich 129 (1996): 33-45.
- Emmett, R. E., Mikkola, H., Mummery, L., & Westerhoff, G. (1972). Prey found in eagle owls' nest in central Sweden. British Birds, 65(11), 482-483.
- Schaefer, J.H. (1970). Womit ernährt der uhu (Bubo bubo) in Lappland seine Jungen. Bonner zoologische Beiträge, 21, 52-62.
- Emikov, E.V. Trophic remains from the Eagle-Owl (BUBO BUBO L) in forest-steppe landscapes of Middle Siberia.
- Donázar, J. A. (1989). Variaciones geograficas y estacionales en la alimentacion del Buho real. Ardeola, 36, 25-39.
- Donazar, D. 1998. Interhabitat differences in the diet of the Eagle Owl (Bubo bubo) in the mid Ebro river valley (NE Spain): effect of European rabbit (Oryctolagus cuniculus) availability. 45 (1): 35-46.
- Sandor, A. D. & Bugariu, S. (2008). Food habits of the Eurasian Eagle Owl (Bubo bubo) in Cheile Dobrogei Gorge. Sc. Annals of DDI, 16: 69-74.
- Simeonov, S., & Boev, Z. (1988). A study of the nutritive spectrum of the eagle owl (Bubo bubo L.) in Bulgaria. Ecology, 21, 47-56.
- Lebl, K., Bieber, C., Adamík, P., Fietz, J., Morris, P., Pilastro, A., & Ruf, T. (2011). Survival rates in a small hibernator, the edible dormouse: a comparison across Europe. Ecography, 34(4), 683-692.
- Milehic, T. (2002). Diet of the Eagle Owl Bubo bubo in southwestern Slovenia. Acrocephalus 23 (112): 81-86.
- Toffoli, R., Beraudo, P., Caula, B., & Pavia, M. (1999). L'alimentazione di una coppia di Gufo reale Bubo bubo sulle Alpi Marittime. AVOCETTA-PARMA-, 23, 102-102.
- Shehab, A. H. (2004). Diet of the Eagle Owl, Bubo bubo, in Syria. Zoology in the Middle East, 33(1), 21-26.
- Obuch, J. (1994). On the food of eagle-owl (Bubo bubo) and tawny owl (Strix aluco) in the eastern part of Turkey. Tichodroma, 7, 7-16.
- Qinghu, C., Jianping, S. & Zhigang, J. (2008). Summer diet of two sympatric species of raptors upland buzzard (Buteo hemilasius) and Eurasian eagle owl (Bubo bubo) in Alpine meadow: Problem of coexistence. Pol. J. Ecol, 56(1), 173-179.
- Tumurbat, J., Sundev, G., & Yosef, R. (2009). Nest site and food composition of the Eagle Owl Bubo bubo in Mongolia. Ardea, 97(4), 519-523.
- Penteriani, V., Gallardo, M., & Roche, P. (2002). Landscape structure and food supply affect eagle owl (Bubo bubo) density and breeding performance: a case of intra-population heterogeneity. Journal of Zoology, 257(03), 365-372.
- Mikkonen, T., Valkama, J., Wihlman, H. & Sukura, A. (2005): Spatial Variation of Trichinella prevalence in rats in Finnish waste disposal sites. Journal of Parasitology 91: 210-213.
- Zahler, P., & Dietemann, C. (1999). A note on the food habits of Eurasian Eagle Owl Bubo bubo in northern Pakistan. Forktail, 98-99.
- "Dietmar Nill Photographer". Retrieved 6 March 2015.
- Wagner, G., & Springer, M. (1970). Zur Ernährung des uhus Bubo bubo im Oberengadin. Orn. Beob, 67, 77-94.
- Leditznig, C., Leditznig, W., & Gossow, H. (2001). 15 Jahre Untersuchungen am Uhu (Bubo bubo) im Mostviertel Niederösterreichs-Stand und Entwicklungstendenzen. Egretta, 44: 45-73.
- Wassink, G. (2010). Het dieet van de Oehoe in Nederland en enkele aangrenzende gebieden in Duitsland. Limosa. 83: 97-108.
- Wilson, E. J., Newson, R. M., & Aliev, F. F. (1966). Enemies and Competitors of the Nutria in USSR. Journal of Mammalogy, 353-355.
- Serrano, D. (2000). Relationship between raptors and rabbits in the diet of eagle owls in southwestern Europe: competition removal or food stress? Journal of Raptor Research, 34(4), 305-310.
- Lourenco, R. (2006). The food habits of Eurasian eagle-owls in Southern Portugal. Journal of Raptor Research, 40(4), 297-300.
- Orsini, P. (1985). The diet of the eagle owl Bubo bubo in Provence, southern France. Alauda, 53(1), 11-28.
- Antonio Martínez, J., & Zuberogoitia, I. (2001). The response of the Eagle Owl (Bubo bubo) to an outbreak of the rabbit haemorrhagic disease. Journal für Ornithologie, 142(2), 204-211.
- Donázar, J., & Ceballos, O. (1989). Selective predation by eagle owls Bubo bubo on rabbits Oryctolagus cuniculus: age and sex preferences. Ornis Scandinavica, 117-122.
- Penteriani, V., Del Mar Delgado, M., Bartolommei, P., Maggio, C., Alonso‐Alvarez, C., & J Holloway, G. (2008). Owls and rabbits: predation against substandard individuals of an easy prey. Journal of Avian Biology, 39(2), 215-221.
- Schweiger, A., & Lipp, L. (2011). Wühlmäuse (Arvicolinae) als bevorzugte Beute des Uhus Bubo bubo während der Jungenaufzucht in Bayern. Zeitschrift bayerischer und baden-württembergischer Ornithologen, 50(1): 1-25.
- Dementiev, G. P., Gladkov, N. A., Ptushenko, E. S., Spangenberg, E. P., & Sudilovskaya, A. M. (1951). Birds of the Soviet Union, vol. 1. Jerusalem: Israel Program for Scientific Translation.
- Adamcik, R. S., Todd, A. W., & Keith, L. B. (1978). Demographic and dietary responses of great horned owls during a snowshoe hare cycle. Canadian Field-Naturalist, 92(2), 156-166.
- Shin, D. M., Yoo, J. C., & Jeong, D. M. (2013). Spatial Variation of Eurasian Eagle-Owl Diets in Wetland and Non-Wetland Habitats in West-Central Korea. Journal of Raptor Research, 47(4), 400-409.
- Dresser, H. E. (1881). A History of the Birds of Europe. Henry E. Dresser.
- Smith, A. T., Formozov, N. A., Hoffmann, R. S., Chapman, J. A., & Flux, J. E. (Eds.). (1990). Rabbits, hares and pikas: status survey and conservation action plan. IUCN.
- Laursen, J. T. (1999). Fødevalg hos Stor Hornugle Bubo bubo i Danmark. Dansk Orn. Foren. Tidsskr, 93, 141-144.
- Förstel, V. A. (1995). Der Uhu Bubo bubo L. in Nordbayern. Zeitschrift bayerischer und baden-württembergischer Ornithologen, 34(2/3): 77-93.
- Papageorgiou, N. K., Vlachos, C. G., & Bakaloudis, D. E. (1993). Diet and nest site characteristics of Eagle Owl (Bubo bubo) breeding in two different habitats in north-eastern Greece. Avocetta, 17(1), 49-54.
- Zemanová, K. (2009). Potrava výra velkého na střední Moravě.
- Malovichko, I.L., Gavrilov, А, I., & Fedosov, V.N. (2007). Characteristics of distribution, breeding and diet of the Eagle Owl in the steppes of Stavropol Territory. Committee on birds of prey in the dynamic environment of the Third Millennium.
- Karyakin, I., Kovalenko, A., Levin, A., & Pazhenkova, A. (2009). Eagle Owl in the Aral-Caspian Region, Kazakhstan. Raptors Conservation, (17).
- Rosina, V. V., & Shokhrin, V. P. (2011). Bats in the diet of owls from the Russian far East, southern Sikhote Alin. Hystrix It. J. Mammal., 22, 205-213.
- Lourenco, R., & Rabaca, J. (2006) Intraguild predation by Eagle Owls in Europe. Airo 16: 63-68.
- Korpimäki, E., & Norrdahl, K. (1989). Avian predation on mustelids in Europe 1: occurrence and effects on body size variation and life traits. Oikos, 205-215.
- Ruiz-Olmo, J., Batet, A., Jiménez, J., & Martínez, D. (2005). Habitat selection by female otters with small cubs in freshwater habitats in northeast Spain. Lutra, 48(1), 45-56.
- Butler, J. M., & Roper, T. J. (1995). Escape tactics and alarm responses in badgers Meles meles: a field experiment. Ethology, 99(4), 313-322.
- Volkov, S.V., Sharikov, A.V. & Morozov, V.V. (2009) Owls in Northern Eurasia.
- Geffen, E. (1994). Vulpes cana. Mammalian Species, 1-4.
- Larivière, S., & Seddon, P. J. (2001). Vulpes rueppelli. Mammalian Species, 1-5.
- Ward, O. G., & Wurster-Hill, D. H. (1990). Nyctereutes procyonoides. Mammalian Species, 1-5.
- Dahmer, T. D. Feral/stray dogs and civet mortality on Kau Sai Chau.
- Sidorovich, V. E. (2011). Analysis of vertebrate predator-prey community. Tesey, Minsk, Ukraine.
- Aliev, F. F., & Sanderson, G. C. (1966). Distribution and status of the raccoon in the Soviet Union. The Journal of Wildlife Management, 497-502.
- Frey, H., & Walter, W. (1984). Zur Ernährung des Uhus, Bubo bubo (Linnaeus 1758), Aves, an einem alpinen Brutplatz in den Hohen Tauern (Salzburg, Österreich). Annalen des Naturhistorischen Museums in Wien. Serie B für Botanik und Zoologie, 91-99.
- Curry-Lindahl, K. Photographic Studies of Some Less Familiar Birds: LXXXIV. Eagle Owl. British Birds, L: 486-490.
- Andrews, Peter (1990) Owls, Caves, and Fossils: Predation, Preservation, and Accumulation of Small Mammal Bones in Caves, with an Analysis of the Pleistocene Cave Faunas from Westbury-sub-Mendip, Somerset, UK University of Chicago Press. 231 pg.
- Levy, N., & Bernadsky, G. (1991). Creche behavior of nubian ibex Capra ibex nubiana in the Negev desert highlands, Israel. Israel Journal of Zoology, 37(3), 125-137.
- Obuch, J., & Karaska, D. (2010). The Eurasian eagle-owl (Bubo bubo) diet in the Orava Region (N Slovakia) . Slovak Raptor Journal, 4, 83-98.
- CRC Handbook of Avian Body Masses, 2nd Edition by John B. Dunning Jr. (Editor). CRC Press (2008), ISBN 978-1-4200-6444-5.
- Bayle, P., & Schauls, R. (2011). Biologie de quatre couples de grand-duc d’Europe Bubo bubo au Luxembourg. Bull. Soc. Nat. luxemb, 112, 51.
- Rockenbach, D. (2005). Der Uhu Bubo bubo in Baden-Württemberg- Wie Phönix aus der Asche! Ornithol. Anz. 44: 117-122.
- Penteriani, V., Sergio, F., del Mar Delgado, M., Gallardo, M., & Ferrer, M. (2005). Biases in population diet studies due to sampling in heterogeneous environments: a case study with the Eagle Owl. Journal of Field Ornithology, 76(3), 237-244.
- Frey, V.H. (1973). Zur Ökologie niederösterreichischer Uhupopulationen. Egretta, 16: 1-68.
- Vondrácek, J. (1983). PUÍSPEVEK К POTRAVitfEKOLÓGH A SLOZENf POTRAVY VYRA VELKÉHO NA SEVEROCESÌCYCH LOKALITÂCH. Sylvia, 22: 39-54.
- Choi, C. (2007). Y.; Nam, H.–Y.; Lee, W.–S. Diets and foraging tactics of Eurasian eagle owls (Bubo bubo) in two different habitat types. Kor. J. Env. Eco, 21, 30-37.
- Vidal, P. & Bayle, P. (1997). Le Grand-Duc d'Europe bubo bubo : Une nouvelle espèce d'oiseau nicheuse sur les îles de Marseille (Bouches-du-Rhône). Faune de Provence, 18: 55-57.
- Kolomiytsev, N.P, & Poddubnaya, N.Y. (2007). The biology of the eagle owl Bubo bubo in the Lazo Nature Reserve (South Primorye) . Russian Ornithological Journal 2007, Volume 16, Issue Express 364: 835-840.
- Vazhov, S. V., Karyakin, I. V., Nikolenko, E. G., Barashkova, A. N., Smelansky, I. E., Tomilenko, A. A., & Bekmansurov, R. H. (2011). Raptors of the Ukok Plateau, Russia. Raptors Conservation, (22).
- Mitev, U. & Boev, H. (2006). Хранителен спектър на бухала (Bubo bubo (L., 1758))(Aves: Strigiformes) в две холоценски находища от Североизточна България. Hist. nat. bulgarica, 17, 149-161.
- Hagen, Y. (1950). Noen iakttagelser over hubro (Bubo bubo L.) i Rogaland. Stav. Mus. Arbok, 93-110.
- Arlettaz, R. (1988). Statut du Hibou grand-duc, Bubo bubo, en Valais central. In Bulletin de la Murithienne (No. 106, pp. 3-24).
- Blonda, R. Dieta del gufo reale Bubo bubo nella provincia del Verbano Cusio Ossola Alpi centro-occidentali italiane: confronto tra diverse tipologie ambientali. Parco Naturale Alpe Veglia e Devero.
- Olalla‐Tárraga, M. Á., Rodríguez, M. Á., & Hawkins, B. A. (2006). Broad‐scale patterns of body size in squamate reptiles of Europe and North America. Journal of Biogeography, 33(5), 781-793.
- Bent, A. C. 1938. Life histories of North American birds of prey, Part 2. U.S. National Museum Bulletin 170:295-357.
- Russ, H. 2010. The Eurasian eagle owl (Bubo bubo): a fish bone accumulator on Pleistocene cave sites? Journal of Taphonomy 8(4): 281-290.
- Mikkola, H. (1983). Owls of Europe. T & AD Poyser Books.
- Herrera, C. M., & Hiraldo, F. (1976). Food-niche and trophic relationships among European owls. Ornis Scandinavica, 29-41.
- Nilsson, I. N. (1984). Prey weight, food overlap, and reproductive output of potentially competing Long-eared and Tawny Owls. Ornis Scandinavica, 176-182.
- Korpimäki, E., & Sulkava, S. (1987). Diet and breeding performance of Ural owls Strix uralensis. Ornis Fennica, 64, 57-66.
- Clark, W. S., & Porter, R. (1999). A field guide to the raptors of Europe, the Middle East, and North Africa. Oxford: Oxford University Press.
- Gil-Sanchez, J. M., Valenzuela, G., & Sanchez, J. F. (1999). Iberian wild cat Felis silvestris tartessia predation on rabbit Oryctolagus cuniculus: functional response and age selection. Acta Theriologica, 44(4), 421-428.
- Mañosa, S. (1994). Goshawk diet in a Mediterranean area of northeastern Spain. Journal of Raptor Research, 28(2), 84-92.
- Viñuela, J., & Veiga, J. P. (1992). Importance of rabbits in the diet and reproductive success of Black Kites in southwestern Spain. Ornis Scandinavica, 132-138.
- Mañosa, S., & Cordero, P. J. (1992). Seasonal and sexual variation in the diet of the common buzzard in northeastern Spain. Journal of Raptor Research, 26(4), 235-238.
- Moreno, S., Beltrán, J. F., Cotilla, I., Kuffner, B., Laffite, R., Jordán, G., & Villafuerte, R. (2008). Long-term decline of the European wild rabbit (Oryctolagus cuniculus) in south-western Spain. Wildlife Research, 34(8), 652-658.
- Delibes, M., Rodríguez, A., & Ferreras, P. (2000). Action plan for the conservation of the Iberian lynx in Europe (Lynx pardinus) (No. 111-115) . Council of Europe.
- Real, R., Barbosa, A. M., Rodríguez, A., García, F. J., Vargas, J. M., Palomo, L. J., & Delibes, M. (2009). Conservation biogeography of ecologically interacting species: the case of the Iberian lynx and the European rabbit. Diversity and Distributions, 15(3), 390-400.
- González, L. M., Bustamante, J., & Hiraldo, F. (1990). Factors influencing the present distribution of the Spanish imperial eagle, Aquila adalberti. Biological Conservation, 51(4), 311-319.
- Ferrer, M., Penteriani, V., Balbontı́n, J., & Pandolfi, M. (2003). The proportion of immature breeders as a reliable early warning signal of population decline: evidence from the Spanish imperial eagle in Doñana. Biological Conservation, 114(3), 463-466.
- Mikkola, H. (1976). Owls killing and killed by other owls and raptors in Europe. British Birds, 69, 144-154.
- Lourenço, R., Santos, S. M., Rabaça, J. E., & Penteriani, V. (2011). Superpredation patterns in four large European raptors. Population ecology, 53(1), 175-185.
- Förstel, A. (1983) Bestandsaufstockung des Uhus Bubo bubo in Bayern. Anzeiger der Ornithologischen Gesellschaft in Bayern, 22, 145–167.
- Solonen, T. (2011). Impact of dominant predators on territory occupancy and reproduction of subdominant ones within a guild of birds of prey. Open Ornithology Journal, 4, 23-29.
- Milchev, B. (2009). Breeding biology of the Long-legged Buzzard Buteo rufinus in SE Bulgaria, nesting also in quarries. Avocetta, 33, 25-32.
- Sergio, F., & Hiraldo, F. (2008). Intraguild predation in raptor assemblages: a review. Ibis, 150(s1), 132-145.
- Hakkarainen, H., & Korpimäki, E. (1996). Competitive and predatory interactions among raptors: an observational and experimental study. Ecology, 1134–1142.
- Sergio, F., Marchesi, L., Pedrini, P., & Penteriani, V. (2007). Coexistence of a generalist owl with its intraguild predator: distance-sensitive or habitat-mediated avoidance? Animal Behaviour, 74(6), 1607–1616.
- Martínez, J. E., Martínez, J. A., Zuberogoitia, I., Zabala, J., Redpath, S. M., & Calvo, J. F. (2008). The effect of intra-and interspecific interactions on the large-scale distribution of cliff-nesting raptors. Ornis Fennica, 85(1), 13.
- Brambilla, M., Rubolini, D., & Guidali, F. (2006). Eagle Owl Bubo bubo proximity can lower productivity of cliff-nesting Peregrines Falco peregrinus. Ornis Fennica, 83(1), 20.
- Sergio, F., Marchesi, L., & Pedrini, P. (2003). Spatial refugia and the coexistence of a diurnal raptor with its intraguild owl predator. Journal of Animal Ecology, 72(2), 232-245.
- Sergio, F., Scandolara, C., Marchesi, L., Pedrini, P., & Penteriani, V. (2005). Effect of agro‐forestry and landscape changes on Common Buzzards (Buteo buteo) in the Alps: implications for conservation. Animal Conservation, 8(1), 17-25.
- Kenward, R. (2006) The Goshawk. Poyser Monographs, Poyser T & AD: London.
- Watson, J. (2010). The golden eagle. Poyser Monographs; A&C Black.
- Cantegrel-Gassiot, L., Pagoaga, A., R. & C., & Rieu, L. (2015). Le Grand-duc d’ Europe Bubo bubo dans les Pyrénées occidentales: état des connai s sances actuel les et bi lan de 10 années de prospections. Le Casseur d’os vol. 14 – 2014, pp. 71-87.
- Tella, J. L., & Mañosa, S. (1993). Eagle owl predation Egyptian Vulture and Northern Goshawk-Possible effect of a decrease in European Rabbit availability. Journal of Raptor Research, 27(2), 111-112.
- Vaassen, E. W. Status and occurrence of Bonelli’s Eagle, Hieraaetus fasciatus, in Turkey and Eastern Mediterranean–A Population Estimate. Raptor Research & Rehabilitation Center Turkey.
- Lourenço, R., Penteriani, V., del Mar Delgado, M., Marchi-Bartolozzi, M., & Rabaça, J. E. (2011). Kill before being killed: an experimental approach supports the predator-removal hypothesis as a determinant of intraguild predation in top predators. Behavioral Ecology and Sociobiology, 65(9), 1709–1714.
- Miltschev, B., & Menzel, J. (2012). Rupfung eines weiblichen Schreiadlers Aquila pomarina durch einen Uhu Bubo bubo. Ornithologische Mitteilungen, 64(1/2), 21-23.
- Gombobaatar, S., Sumiya, D., Shagdarsuren, O., Potapov, E., & Fox, N. (2004). Saker Falcon (Falco cherrug milvipes Jerdon) mortality in Central Mongolia and population threats. Mongolian Journal of Biological Sciences, 2(2), 13-21.
- Ellis, D. H., Tsengeg, P., Whitlock, P., & Ellis, M. H. (2000). Predators as prey at a Golden Eagle Aquila chrysaetos eyrie in Mongolia. Ibis, 142(1), 139-142.
- Vazhov, S. V., Bachtin, R. F., Barashkova, A. N., & Smelansky, I. E. (2013). On the Study of the Steppe Eagle in the Altai Kray, Russia. Raptors Conservation, (27).
- López-López, P., García-Ripollés, C., Giménez, J., & Urios, V. (2016). A Case of Predation of a Eurasian Eagle-Owl by a Bonelli's Eagle. Journal of Raptor Research, 50(4), 422-424.
- Jaume, S. (2000). Depredaciones de Zorro Vulpes vulpes sobre Búho Real Bubo bubo en un área del litoral Ibérico. Ardeola, 47(1), 97-99.
- Görner, M. (2005). Zur Ernährungssituation des Uhus (Bubo b. bubo L.) in Thüringen: Brutbiologie, Ernährung, Prädation. Ornithol. Anz. 44: 137-139.
- Rasmussen, Uffe. "UTROLIG VIDEO: Ugleunger dræbt for åben skærm". Dansk Ornitologisk Forening. Retrieved 9 May 2017.