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Javan hawk-eagle


The Javan hawk-eagle (Nisaetus bartelsi) is a medium-sized in the family , endemic to the island of in , where it inhabits humid lowland and montane forests.
Adults measure 56–70 cm in length, possess a wingspan of 110–130 cm, and weigh 1.1–1.6 kg, featuring dark brown plumage, a pale cream-colored , and a prominent crest on the head that distinguishes it from similar .
It forages primarily from perches in the forest canopy, preying on birds, small mammals, reptiles, and amphibians captured on the ground or in trees.
Classified as Endangered on the , the faces severe threats from ongoing loss and fragmentation, with a global population estimated at 600–900 mature individuals confined to disjunct forest patches.

Taxonomy

Classification and etymology

The Javan hawk-eagle (Nisaetus bartelsi) is a member of the order and family , the latter encompassing diurnal such as hawks, eagles, and vultures. Its full taxonomic classification is: Kingdom Animalia, Phylum Chordata, Class Aves, Order , Family , Genus Nisaetus, and Species N. bartelsi. Originally described as Spizaetus bartelsi by German ornithologist Erwin Stresemann in based on specimens collected in , the species was reclassified into the genus Nisaetus following molecular phylogenetic studies in the early 2000s that analyzed one nuclear and two mitochondrial genes, revealing a distinct of Asian "hawk-eagles" separate from Neotropical species retained in . The genus name Nisaetus derives from the Medieval Latin nisus (referring to a ) combined with the aetos (), denoting its intermediate morphology between these raptors. The specific epithet bartelsi commemorates the Bartels family, a group of naturalists and plantation owners based in western who collected the type specimens and provided early observations of the species' behavior and in the , including records from the slopes of Mount Gede. Due to variability in Spizaetus-like across specimens, the Javan hawk-eagle was not fully recognized as a distinct species until 1953, when additional field data confirmed its separation from congeners like the (N. cirrhatus).

Phylogenetic relationships

The Javan hawk-eagle (Nisaetus bartelsi) belongs to the family within the order , specifically in the subfamily , known as the booted eagles due to their feathered tarsi. Phylogenetic analyses using both mitochondrial and nuclear DNA markers have resolved the booted eagles into five major monophyletic genera: Nisaetus (10 species), (4 Neotropical species), Clanga (3 species), (9 species), and (6 species). Within this framework, Nisaetus bartelsi is placed in the genus Nisaetus, which encompasses crested hawk-eagles primarily distributed across and the ; this genus is supported by high bootstrap values across seven genetic loci, including , NADH subunits, and control region sequences, confirming its distinct evolutionary lineage from other aquiline eagles. Earlier molecular studies based on (e.g., and control region) revealed in the traditionally broad genus Spizaetus, with Asian such as N. bartelsi clustering separately from Neotropical hawk-eagles, indicating in and morphology rather than shared ancestry. Subsequent analyses of and cyt-b genes specific to N. bartelsi demonstrate its divergence from close relatives like the (Nisaetus cirrhatus), with genetic distances supporting its status as a distinct endemic restricted to , consistent with driven by island isolation. This positioning underscores N. bartelsi's basal role within Nisaetus, reflecting ancient vicariance events in .

Physical characteristics

Morphology and plumage variation

The Javan hawk-eagle (Nisaetus bartelsi) is a medium-sized measuring 60-70 cm in total length, with a slender build characterized by short, rounded wings and a long tail. Its wingspan ranges from 110 to 130 cm, and adults weigh between 1100 and 1600 grams, with females larger and more robust than males while retaining an overall slender appearance. The species possesses a prominent of 2-4 long black feathers, up to 12 cm in length with white tips, which can appear fan-shaped or pointed. Adult plumage features dark brown upperparts, including a and chestnut-brown head with a yellow-brown that appears in . The throat is nearly pure white, bordered by dark brown to black moustachial stripes and a mesial stripe, while underparts are whitish-buff to white, with bold dark brown drop-shaped marks on the breast and narrow dark brown barring on the belly. The back and upperwings are dark brown with buff margins and black-tipped primaries; the tail upperside shows dark brown with four black bands and a thin white terminal band, while the underside is greyish-buff with four brown bands. In flight, adults display bold black banding on and tail, with a chestnut head contrasting the darker body and wings held in a slight V-shape. Plumage variation primarily occurs with age, as juveniles differ markedly from . Juveniles have cinnamon-brown head and lacking contrasting stripes, pale tan underparts, a shorter , and paler black banding on wings and tail, with white wings featuring grey-buff primaries, cinnamon-brown underwing-coverts, and an incomplete triangular white patch at the carpal joint. The juvenile tail underside is greyish-buff with only the outer dark brown band visible, and the is bluish-grey, darkening to brown only in downy chicks. Immatures in their second year develop a , darkening , and emerging tail bands, with progressive barring on underparts and potential development of moustachial and mesial stripes over subsequent years, reaching full in 5-6 years as breast lightens to white with drop-shaped marks. Juveniles exhibit a slightly smaller and longer tail relative to . Unlike some congeners such as the , no distinct color morphs are reported for N. bartelsi, with variation largely ontogenetic rather than polymorphic.

Sexual dimorphism and measurements

The Javan hawk-eagle exhibits reversed , with females larger and more robust than males, a trait common among accipitrids that facilitates niche partitioning in and reduces intrasexual . This dimorphism is moderate in degree, enabling field by experienced observers through differences in overall size during flight or perched postures, though patterns remain similar between sexes. Measurements from museum skins confirm statistically significant size disparities, though precise ratios vary by trait; for instance, analyses of 23 specimens indicate females exceed males in linear dimensions such as wing chord and . Adult body length ranges from 56 to 70 cm, with females typically 10-15% longer than males and attaining the upper end of this spectrum. measures 110-142 cm, correlating positively with sex-specific body mass differences. Body mass varies from 960 to 1,650 g, again with females heavier to support reproductive demands like production and . Tarsus length and other skeletal metrics follow similar patterns, though data remain limited due to the species' rarity and ethical constraints on live measurements.

Distribution and habitat

Geographic range

The Javan hawk-eagle (Nisaetus bartelsi) is endemic to the island of , , where it inhabits fragmented patches of remaining humid . Its distribution spans the length of the island, from coastal lowlands to montane regions at elevations up to 3,000 meters, though it is now primarily restricted to steep slopes, ridges, and protected mountainous areas due to lowland habitat loss from and . Confirmed presence occurs in at least 22 discrete forest blocks, including key sites in such as Gunung Halimun Salak National Park, Central Java's and Dieng regions, and East Java's , Meru Betiri National Park, and Sempu Island. The estimated extent of occurrence covers approximately 147,000 km², but suitable habitat has contracted significantly, with populations isolated by . Although some assessments mention possible occurrence on adjacent based on unconfirmed sight reports, such as from Bali Barat National Park, no populations or verified recent records exist there, and the is widely regarded as absent from the island.

Habitat preferences and requirements

The Javan hawk-eagle (Nisaetus bartelsi) primarily inhabits humid tropical primary forests on , where it utilizes both nesting and hunting grounds, though secondary forests are also employed for these purposes. Due to widespread lowland , remaining populations are largely confined to steeper slopes, ridges, and montane regions, reflecting a shift from former broader lowland distributions. The species prefers subtropical and tropical moist lowland forests, extending into montane forests up to elevations of 200–1,200 m, with records spanning from to 3,000 m. Habitat requirements emphasize structurally complex forests with tall, mature trees suitable for nesting platforms, typically constructed in remnant primary or secondary stands. Proximity to open edges or bordering cultivated areas and plantations facilitates hunting of arboreal prey, as the eagle opportunistically forages in such adjacent zones when core forest habitat is available. Adults exhibit a strong preference for closed-canopy evergreen forests, with lesser use of secondary growth, whereas juveniles and immatures disproportionately occupy disturbed, open habitats during dispersal phases, suggesting age-specific tolerances for suboptimal conditions. The demonstrates adaptability to fragmented landscapes, persisting in isolated patches as small as 3,000 , provided they retain sufficient canopy cover and prey density. Core home ranges require at minimum 600 of contiguous to support territorial needs, underscoring the causal link between habitat patch size and viability amid ongoing fragmentation pressures. Nesting occurs predominantly on steep slopes (e.g., 65° inclines) at mid-elevations around 1,100–1,300 m near natural edges, prioritizing sites with and overlook of territories.

Behavior and ecology

Foraging and diet

The Javan hawk-eagle employs a perch-hunting strategy, typically positioning itself in the forest canopy to scan for prey before launching swift, stealthy attacks using its sharp talons to capture and immobilize targets. This method suits its forested , allowing exploitation of arboreal and vertebrates. Observations indicate peak activity periods for scanning and pursuit between 09:00 and 12:00, with flying comprising 29% of daily contrasted against 71% perching. Its diet is carnivorous and opportunistic, dominated by small to medium-sized vertebrates including , mammals, and reptiles. During the nestling period, parents deliver a diverse array of prey to the nest, totaling 109–116 items over 68–72 days, with males provisioning more in mornings and females in afternoons. Mammals constitute a key component, encompassing squirrels (family Sciuridae), treeshrews (family Tupaidae), (family ), and bats (order Chiroptera); birds and reptiles supplement this, reflecting adaptation to Java's prey availability. Peak feeding occurrences align with late afternoon (14:00–17:00), potentially tied to prey activity cycles and reduced human disturbance.

Reproduction and breeding biology

The Javan hawk-eagle (Nisaetus bartelsi) is monogamous, forming long-term pair bonds, with individuals reaching at three to four years of age. occurs irregularly throughout the year but predominantly between and , aligning with periods of resource availability in its forested . Pairs typically every two years, reflecting a low reproductive rate characteristic of many large raptors, which limits population recovery potential. Nests are constructed in the upper canopy of tall, emergent trees within primary or mature secondary forests, using sticks lined with green leaves and softer materials for structure and . Nest sites are selected for their height and isolation, providing protection from ground predators and human disturbance, though has reduced suitable locations. Clutches consist of a single , laid in a shallow within the nest, which supports the species' K-selected strategy emphasizing investment in few offspring. Incubation lasts approximately 47 days (range 46-48 days), performed primarily by the female while the male provisions her with prey at the nest. Upon , the female participates in hunting, and both parents feed the chick, which remains dependent on them for several months post-fledging, with full independence achieved after about three to four months. This extended , combined with the single-egg , underscores the vulnerability of breeding success to habitat loss and nest predation.

Territoriality and social behavior

The Javan hawk-eagle exhibits strong territoriality, maintaining exclusive ranges estimated at a mean of approximately 400 hectares, derived from direct observations over 67 hours across sites like Halimun ( distance of 1.8 km yielding 254 ha), Gede-Pangrango (530 ha), and radiotelemetry of an adult male in Mountains (300 ha using minimum and methods during nonbreeding season from 31 March to 15 May 1998). Nest spacing between territories averages 1.8–3 km, corresponding to areas of 314–710 ha, which supports foraging needs in contiguous forest habitats while minimizing overlap with conspecifics. Territorial defense intensifies during , involving aerial displays such as soaring prominently above the canopy to signal boundaries, with observed interactions between neighboring pairs indicating active boundary maintenance rather than passive exclusion. Home-ranges show partial overlap with sympatric raptors like changeable hawk-eagles and , but core areas remain defended against intrusions by other Javan hawk-eagles, ensuring resource exclusivity for pair and offspring survival. Social structure centers on monogamous pairs that co-occupy territories year-round, with juveniles dispersing after remaining dependent on parents for at least one year post-fledging, fostering cohesion during early independence. Beyond breeding pairs and attendant young, individuals are typically solitary, exhibiting minimal gregariousness or cooperative hunting, consistent with observations of lone or paired occupancy in forest patches. Pair bonds facilitate joint and chick provisioning, though no evidence supports or larger social units.

Conservation status

Population dynamics and estimates

The Javan hawk-eagle (Nisaetus bartelsi) population is estimated at 511 breeding pairs as of , equating to approximately 1,022 individuals assuming a 1:1 adult-to-juvenile ratio, distributed across 38 confirmed occupied habitat patches totaling 10,166 km² on Island. This figure represents an increase from 325 pairs estimated in 2009, derived from habitat distribution modeling combined with patch occupancy surveys that accounted for detection probabilities and habitat suitability. Earlier assessments, such as a 2001 survey, placed the breeding population at 137–188 pairs (600–900 total birds) across 22 discrete blocks, highlighting underestimation in prior counts due to incomplete survey coverage. Population dynamics are characterized by fragmentation into isolated patches amid ongoing deforestation, with occupancy varying by patch size and connectivity; larger patches (>500 km²) support higher densities, while smaller ones (<100 km²) exhibit lower persistence. The species' effective population size remains low, with mature individuals numbered at 300–1,200 and a continuing decline inferred from habitat loss rates exceeding recruitment, though recent data suggest potential stabilization if fragmentation effects are mitigated. Density estimates from targeted studies indicate 0.77 individuals per km² or 2.83 km² per pair in suitable forest, underscoring sensitivity to edge effects and isolation. Projections under business-as-usual scenarios predict further contraction, with habitat projected to shrink by 40% by 2050 due to pressures, potentially reducing pair numbers below viable thresholds without intervention. assessments classify the as severely fragmented, with trends monitored via repeat occupancy modeling to detect shifts in success and dispersal limitations.

Primary threats and causal factors

The primary historical threat to the Nisaetus bartelsi, or Javan hawk-eagle, has been the extensive destruction and fragmentation of its lowland and montane forest habitats on , , primarily driven by conversion to , commercial , , and expanding human settlements. These activities have reduced contiguous forest patches, isolating populations and limiting dispersal, with rates on Java exacerbating the ' vulnerability due to its dependence on large, undisturbed territories for hunting and nesting. In recent assessments, illegal and trade for the pet market have emerged as the most acute current , with birds captured using methods like snares and baited traps, often facilitated by weak enforcement of Indonesia's protection laws despite the ' designation as a national rare animal in 1993. for trophies or conflict with further compounds direct mortality, while indirect pressures from degradation—such as in fragmented forests increasing exposure to human disturbance—persist as causal factors rooted in unchecked and inadequate land-use regulation. Emerging risks include climate change-induced shifts in prey availability and forest composition, alongside ongoing illegal activities like uncontrolled fires and resource extraction in protected areas, which collectively hinder recovery despite the species' restricted range of approximately 120,000 km² and estimated global of fewer than 700 mature individuals. These threats are interconnected, with habitat loss enabling easier access for trappers and amplifying the eagle's low reproductive rate—typically one chick per pair every two years—as a limiting biological factor.

Conservation efforts and outcomes

Conservation efforts for the Javan hawk-eagle (Nisaetus bartelsi) have primarily focused on habitat protection, population monitoring, and awareness initiatives led by government agencies and non-governmental organizations. In 1998, Indonesia issued a recovery plan for the , followed by a strategic plan emphasizing ecological research and management. A 10-year conservation plan was established in 2013, with the declared a priority in 2015, aiming to increase its population by 10% from a 2019 baseline through measures like enforcement and patrols. Community-based programs, including local workshops and training, have been implemented to raise awareness and reduce illegal trade and hunting, particularly in fragmented habitats. Ex-situ breeding efforts, such as those initiated by PT Smelting in 2018, seek to bolster captive populations for potential reintroduction, while satellite tracking projects since 2021 have mapped movement patterns to inform habitat connectivity strategies. Despite these initiatives, outcomes remain limited, with the species retaining its Endangered status on the due to persistent loss and low viability. As of 2025, the estimated stands at approximately 511 breeding pairs across 74 patches, reflecting no substantial from prior estimates and ongoing fragmentation from and . Monitoring in areas like Gunung Halimun Salak National Park has documented breeding attempts but highlights challenges from and land conversion, with actions yielding only localized successes in nest protection rather than range-wide . Comprehensive attention over the past 25 years has improved data on distribution and threats but has not reversed declines, as pressures continue to constrain effective .

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