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Edwards's pheasant

Edwards's (Lophura edwardsi) is a medium-sized galliform bird endemic to the lowland evergreen forests of .
Males measure 58–65 cm in length, exhibiting glossy blue-black plumage with green fringes on the upperwings, a short white , and scarlet facial skin, while females are smaller with drab chestnut-brown feathers lacking a .
The inhabits secondary forests up to 300 m elevation, characterized by dense , palms, , and , where it forages on the ground for , seeds, and fruits.
Listed as (Possibly Extinct) on the since 2012, with the global wild population estimated at 0–49 mature individuals and no confirmed records since 2000 despite intensive surveys across its historical range in provinces such as Ha Tinh, Quang Binh, Quang Tri, and Thua Thien Hue.
Severe declines stem from habitat loss due to , agricultural expansion, and wartime herbicide use, compounded by direct via wire snares and potential hybridization with the introduced crested fireback (Lophura nycthemera).
relies on a population exceeding 1,400 individuals worldwide, listed under Appendix I, with ongoing feasibility studies for reintroduction into protected areas.

Taxonomy

Discovery and etymology

The first known specimens of Edwards's pheasant (Lophura edwardsi) were obtained from central Annam (present-day central Vietnam) around 1895 and formally described to science in 1896 by French ornithologist Émile Oustalet in the Bulletin du Muséum d'Histoire Naturelle. Oustalet named the species Gennaeus edwardsi based on four skins—three males and one female—deposited in the Muséum National d'Histoire Naturelle in Paris, marking the initial empirical record of this endemic pheasant from seasonal tropical forests. The epithet edwardsi commemorates Alphonse Milne-Edwards (1835–1900), a prominent French zoologist specializing in fossil birds and mammals who served as director of the Muséum National d'Histoire Naturelle from 1890; the naming reflects his broader patronage and institutional influence in ornithology rather than any specific contribution to the collection or study of this taxon. Early 20th-century taxonomic revisions shifted the species from Gennaeus—a genus then encompassing various jungle fowl-like pheasants—to Lophura, recognizing shared morphological features such as elongated frontal crests and overall body structure with congeners like the Kalij pheasant (L. leucomelanos), based on comparative examinations of preserved specimens. These reclassifications preceded modern phylogenetic analyses and relied primarily on osteological and plumage traits observable in limited historical material.

Classification and phylogenetic relationships

Edwards's pheasant (Lophura edwardsi) is classified in the order , family , and genus Lophura, which includes several pheasants native to . The species is monotypic, lacking recognized , as morphological variation within populations does not warrant subspecific division. Historically classified in monotypic genera such as Delacourigallus or Hierophasis, L. edwardsi was transferred to Lophura following molecular evidence from sequences, including cytochrome b and control region genes, which demonstrated phylogenetic clustering with congeners like the (L. nycthemera). Limited genetic samples, constrained by the species' rarity, have necessitated reliance on morphological distinctions—such as the absence of white tail feathers unique to L. edwardsi among Lophura—to differentiate it from relatives, though analyses confirm close Indo-Chinese affinities. The imperial pheasant (L. imperialis), long debated as a valid , was identified via genetic markers as a between L. edwardsi and L. nycthemera, originating from captive founders in 1924 and perpetuated in aviaries. Likewise, the L. hatinhensis (formerly Vietnamese pheasant), described in 1975 and variably treated as a or until the , was synonymized with L. edwardsi after specimen reviews revealed it as an unstable plumage variant rather than a distinct . These resolutions underscore hybridization risks in captive populations and the primacy of integrated morphological-genetic approaches for Lophura .

Physical characteristics

Morphology and sexual dimorphism

Edwards's pheasant (Lophura edwardsi) displays moderate sexual size dimorphism, with males measuring 58–65 cm in total length and weighing 1.1–1.115 kg based on limited specimens, while females are comparably sized but lighter at approximately 1.05 kg. Males exhibit longer tails (24–26 cm) than females (20–22 cm), and male wing length ranges from 22–24 cm compared to 21–22 cm in females. The tarsus measures about 7.5 cm in males, indicative of robust hindlimbs suited for ground-based locomotion. Both sexes share a sturdy, short adapted for probing and vegetation, extensive bare facial , and legs and feet. Wings are rounded with 10 primaries, enabling explosive short-distance flight from the forest floor, though the species is predominantly terrestrial. Males possess hindleg spurs for territorial and combat, which are absent in females, alongside a small crest of elongated feathers atop the head. Sexual dimorphism extends to structural traits beyond size, with males showing greater ornamentation including the and spurs, patterns observed in skins and captive individuals that align with intrasexual and attraction in phasianids. These differences are documented primarily from historical specimens and ex situ populations, as wild observations remain scarce due to the ' rarity.

Plumage and coloration

Adult males display glossy black characterized by a strong metallic blue gloss across the body, particularly evident on the upperparts. The upperwing-coverts exhibit contrasting metallic green fringes, while the facial skin features prominent red wattles. In the nominate L. e. edwardsi, a white crest adorns the head. Adult females possess a duller chestnut-brown plumage, with grey tints on the head, neck, and underparts; breast feathers show buff-colored shafts creating streaked patterns. The wings appear reddish-chestnut, and the crest is shorter and less pronounced than in males, with minimal iridescence overall, facilitating concealment in forest understory environments. Juveniles closely resemble females in their predominantly brown coloration but feature softer, less defined feathering. Chicks exhibit golden-brown with heads marked by dark eye stripes. Male juveniles transition to adult within the first year, with blue feathers first appearing on the and chest around 12 weeks of age. No evidence indicates seasonal variations in for this .

Habitat and distribution

Preferred habitats

Edwards's pheasant (Lophura edwardsi) primarily inhabits lowland forests below 300 m , where year-round high and rainfall support dense understorey essential for cover and foraging. These forests feature closed canopies with abundant dwarf , palms, and scattered bamboo patches, which the utilizes for concealment amid minimal disturbance. Historical records from early 20th-century specimen collections indicate a preference for level or gently sloping terrain within these habitats, rather than steep rocky slopes or open grasslands, which lack sufficient vegetative density. The avoids high-altitude pine-dominated stands, favoring broadleaf formations with thick leaf litter layers that facilitate ground-level movement and predator evasion. Microhabitat suitability is tied to undisturbed undergrowth, including lianas and palms, as observed in pre-deforestation sites yielding the original type specimens.

Historical and current range

Edwards's pheasant (Lophura edwardsi) was historically distributed across , with documented records confined to the provinces of Hà Tĩnh, Quảng Bình, Quảng Trị, and . Specimens were collected from at least eight localities in the late 19th and early 20th centuries, including sites around and Đà Nẵng (formerly Tourane), where the species was described as locally fairly common. During a 1923 expedition, trappers obtained 10 skins and 22 live individuals primarily from , with additional collections of 20 birds from Quảng Trị, five from Thừa Thiên Huế, and one from Quảng Bình in subsequent years. The species' range contracted sharply over the due to factors including habitat loss and hunting, with no confirmed wild individuals observed since 2000, when a group including two males, one female, and four eggs was encountered by rattan collectors in Hải Lăng District, . Subsequent targeted and opportunistic surveys across the historical range, encompassing approximately 500,000 camera-trap nights from 2005 to 2023, have produced no verifiable detections, leading to assessments estimating the wild mature population at 0–49 individuals or classifying the species as possibly . No evidence exists of range expansion, vagrant records beyond , or recolonization of former sites; captive populations thus constitute the principal genetic reservoir pending confirmation of any undetected wild remnants.

Ecology and behavior

Diet and foraging

Edwards's pheasant (Lophura edwardsi) maintains an omnivorous diet inferred primarily from analyses of related species, as direct observations and contents from wild individuals are limited due to the bird's rarity. Components likely include (approximately 33%), grains (26%), (20%), leaves and grasses (10%), and berries or fruits (10%). Invertebrates such as , , and other form a notable portion, alongside matter foraged from the . The species forages terrestrially by scratching and pecking through leaf litter on the forest floor, with activity peaking in early morning and late afternoon. This behavior occurs in pairs or small groups, focusing on uncovering seeds, fruits, and invertebrates without evidence of arboreal feeding. Sparse data preclude firm conclusions on seasonal variations, though captive observations of congeners suggest potential shifts toward greater plant consumption during resource scarcity.

Reproduction and breeding

Edwards's pheasants (Lophura edwardsi) typically form monogamous pairs that exhibit long-term bonding in captivity, with new pairs introduced prior to December to foster compatibility and reduce aggression. Although primarily paired, polygamous groupings have been documented in some settings. activity peaks from late to May in captive populations, coinciding with increased male displays such as wing-whirring, crest-raising, and back-feather fluffing to attract females. These behaviors intensify during the season, remaining strictly diurnal, though wild timing and displays remain largely unobserved. Nests consist of simple ground scrapes, often under cover in captivity or thick undergrowth in simulated wild conditions, lined with leaves or debris. Females lay 4–7 eggs per at intervals of 36–48 hours, with eggs measuring approximately 45 × 36 mm and colored pinkish-buff with sparse white spots denser at the poles; wild clutches may average 5–7 eggs based on rare observations. , performed exclusively by the female after clutch completion, lasts 21–23 days, during which eggs lose an average of 5–6 g in weight. Hatchlings are precocial, capable of following parents shortly after emerging, with females primarily handling rearing duties including brooding for the first day post-hatch and providing protection. Some males assist in care, while others display necessitating separation. In captivity, parent-rearing is recommended and achieves high success, with hatching rates from fertile eggs often exceeding 90%, though overall fertility averages around 52% of laid eggs; wild clutch success and juvenile survival rates, potentially impacted by predation, are unknown due to scant field data.

Vocalizations and social displays

Edwards's pheasants produce low-volume vocalizations adapted to dense environments, with limited documentation primarily from captive observations and sparse reports. Males emit repetitive territorial cries, described as special calls during the season (February–March), to signal territory occupancy. These include short, high-pitched screams, often accompanied by rapid wing flapping, particularly prior to or egg-laying. Alarm calls consist of low "uk uk uk uk uk" sequences or subdued, hard "puk puk puk puk puk" repetitions. Females produce softer clucks, while males may use near-silent clucking-like sounds when approaching females. The species exhibits a restricted vocal compared to more vocal congeners in the genus Lophura, with no loud advertising calls typical of open-habitat pheasants. Social displays emphasize visual and subtle auditory cues over elaborate communal leks, aligning with a primarily solitary or paired . Males perform wing-whirring displays, producing audible whirring sounds detectable only at close range, as part of territorial and signaling. These displays integrate vocal elements, such as the aforementioned screams, to attract mates or deter rivals, though detailed field observations remain scarce due to the bird's rarity. No evidence exists for large lekking aggregations, distinguishing it from some other phasianids. Recordings of these behaviors are predominantly from captivity, with early 20th-century accounts providing minimal additional insights.

Conservation

Primary threats

The primary threats to Lophura edwardsi are habitat loss and degradation combined with intensive hunting pressure. driven by and agricultural expansion has progressively reduced suitable forest cover in , with remaining habitats suffering acute and extensive defoliation during the (1955–1975), when approximately 72 million liters of herbicides, including , were sprayed over affected areas. Subsequent fragmentation from war-related damage, ongoing , and clearance for farming has further isolated remnant forest patches, rendering them less viable for the species' ground-dwelling habits. Hunting by local communities using snares, guns, and traps for and constitutes a major ongoing peril, often indiscriminate and exceeding any sustainable levels given the pheasant's low reproductive output and slow population recovery. While or climate variability have been hypothesized as factors, surveys indicate negligible impacts from or predation by non-native fauna, and no links climatic shifts directly to the ' decline as a primary driver.

Population status and assessments

The wild population of Lophura edwardsi is considered possibly extinct, with no confirmed sightings since 2000 despite extensive surveys across central Vietnam's historical range. In 2024, the IUCN Red List upgraded its status to Critically Endangered (Possibly Extinct in the Wild), reflecting the absence of verifiable evidence such as photographs, specimens, or unambiguous vocalizations from camera traps and field efforts conducted over multiple years. Prior estimates placed the wild population at 50–249 mature individuals, primarily of the nominate subspecies, but these figures predate the lack of detections and are now viewed skeptically given survey failures. Unconfirmed reports of calls or brief glimpses persist, fueling debate on whether inadequate survey coverage in dense, fragmented forests explains the null results or if local extirpations from historical pressures have led to ; empirical data, including repeated non-detections, support elevating risk assessments over optimistic persistence claims. In contrast, the global captive population remains stable at approximately 1,400 individuals as of December 2023, distributed across zoos and breeding facilities in , , and . Genetic management through international studbooks, initiated in the , has preserved diversity by screening maternal lineages and purging hybrids, ensuring the stock derives from fewer than 30 wild founders captured between 1924 and 1930. This ex situ assurance population provides a baseline for potential recovery, though its long-term viability depends on addressing evidenced in breeding records.

Captive breeding and reintroduction efforts

Captive breeding programs for Edwards's pheasant (Lophura edwardsi), also referred to as the Vietnam , were initiated in the 1920s, with the first successful hatching of five chicks from eggs laid on March 23, 1925, by specimens collected by Jean Delacour. These efforts expanded through private and institutional collections, establishing a global captive population exceeding 1,000 individuals derived from an initial founder base of 28 birds imported between 1924 and 1930. Regional management via the European Endangered Species Programme (EEP), accepted by EAZA in 1994, and the AZA (SSP) emphasizes genetic diversity, including the removal of 85 hybrid individuals and incorporation of wild genetics, such as a male captured in the and paired at Zoo. protocols yield clutches of 4–7 eggs with periods of 21–22 days (up to 29 days recorded), prioritizing parent-rearing to preserve natural behaviors and counter risks from the limited founder pool. Reintroduction strategies focus on sites like Pu Mat National Park, identified in the 2015–2020 for habitat reinforcement pending restoration and feasibility assessments targeted for 2020, with goals for sustainable wild subpopulations by 2030. Preparation includes (e.g., aviaries with perches), dietary supplementation with live prey, multi-generational parent-rearing, and intensive anti-predator training simulating aerial and terrestrial threats, alongside soft-release protocols of at least 50 days for site familiarization. Recommendations specify releasing groups of at least 300 birds per site over five years, selected for social cohesion (e.g., parent-guided offspring at ~4 months old), with post-release support such as predator relocation and multiple enclosure stations. In 2025, conservation actions advanced with birds from European facilities, including a female hatched at BIOPARC Fuengirola designated for Vietnam's reintroduction program, and testing of tail-mounted telemetry at Chester Zoo to enable tracking during soft releases. Despite robust captive reproduction, rewilding faces empirical hurdles, including ontogenetic maladaptations after over 35 generations in captivity—manifesting as deficient anti-predator responses—and persistent habitat degradation, which undermine survival without verified wild detectability since 2000. These factors highlight a disparity between ex-situ viability and the prerequisites for effective field reinforcement, necessitating habitat readiness evaluations prior to scaled releases.

References

  1. [1]
    Vietnam Pheasant Lophura Edwardsi Species Factsheet
    It is classified as Critically Endangered (Possibly Extinct). There have been no recent records of Lophura edwardsi despite extensive surveys.
  2. [2]
    Edwards's Pheasant - Lophura edwardsi - Birds of the World
    Mar 4, 2020 · CRITICALLY ENDANGERED. CITES I. Restricted-range species: occurs in Annamese Lowlands Endemic Bird Area, being known only from tiny area of C ...
  3. [3]
    [PDF] EAZA Best Practice Guidelines Vietnam pheasant (Lophura edwardsi)
    Mar 20, 2020 · The Edwards's pheasant (Lophura edwardsi) was described for the first time by Oustalet in 1896 from four skins (3 males and 1 female) which ...
  4. [4]
    Pheasant Avicultural Notes - APWS Birds
    Edwards' Pheasant. Scientific Name: Gennaeus edwardsi. Origin of Name: edwardsi after Alphonse Milne-Edwards, zoologist and director of the Paris Museum of ...
  5. [5]
    About Vietnam Pheasant
    Conservation status​​ They are listed as "Critically Endangered" on the IUCN Red List and many field researchers believe that they are now extinct in the wild ...
  6. [6]
    Genetic diversity, phylogenetic relationships and conservation of ...
    May 11, 2010 · sivinhoii. Edwards's Pheasant is more closely related to Vietnamese Pheasant L. hatinhensis and Imperial Pheasant L. imperialis than to several ...
  7. [7]
    Phylogenetic Relationships of the Phasianidae Reveals Possible ...
    The phylogenetic relationships of 21 pheasant and 6 non-pheasant species were determined using nucleotide sequences from the mitochondrial cytochrome b gene.
  8. [8]
    Evolution of the Mitochondrial DNA Control Region and Cytochrome ...
    Genetic diversity, phylogenetic relationships and conservation of Edwards's Pheasant Lophura edwardsi. Bird Conserv. Int., 9 (1998), pp. 395-410. View in ...
  9. [9]
    Hybrid origin of the imperial pheasant Lophura imperialis (Delacour ...
    Abstract. The imperial pheasant Lophura imperialis was described in 1924 from a captive pair that was obtained in Vietnam, and that became the sole founder.
  10. [10]
    Vietnam Pheasant | Saint Louis Zoo
    Chicks have golden brown plumage. Adults are about half the size of wild turkeys, with the male having distinctive all-black plumage with a blue gloss and ...
  11. [11]
    [PDF] Vietnam Edwards's Pheasant Working Group Action Plan for the ...
    Breeding A very young juvenile was collected on 15 April 1926 at Hue and reared by. Pierre Jabouille (specimen in Muséum National d'Histoire Naturelle, Paris, ...
  12. [12]
    [PDF] Is Edwards's Pheasant Lophura edwardsi extinct in the wild?
    Remaining native forest in the range of Edwards's Pheasant is almost entirely to be found above 300 m, on very steep slopes and/or on karst outcrops, and ...
  13. [13]
    In Search of the Stunning—and Possibly Extinct—Edwards's Pheasant
    W. e peeled off Highway 9 to find a nondescript village called Kreng, which had played a small but vital part in the story of Lophura edwardsi. I'd gone ...
  14. [14]
    Vietnamese Pheasant - CRITTERFACTS
    As omnivorous birds, they consume a diverse range of foraged foods, including seeds, berries, leaves, worms, termites, and other insects.
  15. [15]
    Edwards's Pheasant (Lophura edwardsi) - Simply Birding
    Aug 19, 2025 · Their diet primarily consists of seeds, fruits, and small invertebrates, which they forage from the forest floor. Conservation Status: From ...
  16. [16]
    Our Research - The Edwards's Pheasant
    It is suggested that the Edwards's Pheasant is monogamous and are usually kept in pairs, however there have been examples of polygamous flocks in parks which ...
  17. [17]
    The reproductive behaviour of Edwards's pheasants in captivity
    Edwards's pheasants breed readily in aviculture and the captive population stands at over 1,000 birds worldwide with plans in development to reintroduce the ...Missing: threats | Show results with:threats
  18. [18]
  19. [19]
    Vietnam Pheasants - National Aviary
    Endemic to just few Central Vietnam regions, its species decline is attributed to habitat loss likely caused by Vietnam War herbicide usage, logging, ...Missing: biology reproduction threats
  20. [20]
    Vietnamese pheasant - Zoo Berlin
    The Vietnamese pheasant has therefore been on the IUCN Red List since 2012, classified as “Critically Endangered”, since 2024 with the designation 'Probably ...
  21. [21]
    [PDF] Is Edwards's Pheasant Lophura edwardsi extinct in the wild?
    Edwards's Pheasant Lophura edwardsi, endemic to the lowland forests of central Vietnam, is classified as Critically Endangered (BirdLife International 2017). ...
  22. [22]
    Preparing captive-bred birds for reintroduction: the case of the ...
    Feb 13, 2020 · The Vietnam Pheasant Lophura edwardsi (including L. hatinhensis) is only known from a small area of central Vietnam, where it occurred in ...
  23. [23]
    Edwards pheasant born at BIOPARC is reintroduced into its habitat
    Feb 27, 2025 · Although it is officially still classified as “Critically Endangered”, the lack of recent records suggests that it should be considered “Extinct ...
  24. [24]
    Vietnam Pheasant Tail Telemetry - Chester Zoo
    Mar 20, 2025 · Vietnam pheasants (Lophura edwardsi) are critically endangered. In 2024, the IUCN officially added the designation “probably extinct in the wild ...<|control11|><|separator|>