This partridge is listed as Near Threatened because, despite its small population and very small range, it occurs at many sites and it is not thought to be declining rapidly owing to the reported tolerance that this species and congeners show to forest degradation.
Sibley, C. G.; Monroe, B. L. 1990. Distribution and taxonomy of birds of the world. Yale University Press, New Haven, USA.
Distribution and populationArborophila davidi
27 cm. Well-marked partridge with bold, black-and-white head markings and orange neck flush. Similar spp. Recalls Bar-backed Partridge A. brunneopectus, but differs primarily by broader black band through eye, black gorget, orange neck flush, broader supercilium behind eye, grey on underparts and larger black flank markings. Voice Territorial call, accelerating series of prruu notes, running into rapid series of up to 70 pwi notes. Also, very rapid tututututututututututu (up to 60 notes). Partner often accompanies with slower, stressed tchew-tchew-tchew-tchew. Weak, airy pher or phu notes when agitated.
is known from southern Vietnam
and eastern Cambodia
. Recent surveys have expanded its known range in Vietnam: it has now been recorded from Cat Tien National Park (NP), Dong Nai Protected Forest Management Board (T. Evans in litt.
2007), Vinh An State Forest Enterprise (SFE), Nghia Trung SFE, Bu Gia Map NP, Bu Dop SFE, Vinh Cu Natural and Historical Reserve and Tan Phu SFE (Nguyen Tran Vy 2006), Da Teh SFE (Nguyen Xuan Dang et al
. 2004), Binh Phouc SFE (Nguyen Xuan Dang and Osborn 2004) and Dak O SFE. It is predicted to occur in a number of other sites and may be widespread in southern Lam Dong, Dong Nai, Binh Duong and Binh Phuoc provinces, where suitable habitat remains (Pilgrim et al
. in prep.). A single bird was camera-trapped in Seima Biodiversity Conservation Area (SBCA), Mondulkiri Province, Cambodia in 2002 (Davidson et al.
2002). The species has been recorded subsequently from the same very locality, but it remains enigmatic in the area, with an inexplicably patchy distribution (E. Pollard in litt
. 2009). Based on current evidence, the area of suitable habitat in Cambodia may be as small as 70 km2
(E. Pollard in litt
. 2009). The species is apparently rare (or perhaps just elusive) in some areas. A slow decline is suspected owing to on-going pressures placed on forest habitats, but the apparent ability of this species (as well as many congeners) to tolerate degraded habitats suggests that current forestry operations are unlikely to represent a major threat. Population justification
The species is now known from many sites in southern Vietnam and one in Cambodia. The area of suitable habitat has been found to be more extensive than was previously thought and given the population densities recorded in several congeners and their ability to persist in degraded habitats it seems likely that the population approaches 10,000 individuals, and it is thus placed in the band 2,500-9,999 individuals. This equates to 1,667-6,666 mature individuals, rounded here to 1,500-7,000 mature individuals.Trend justification
This species is assumed to have declined owing to clearance within its very small range, but it is probably tolerant to some degree of forest degradation. Declines are thought to be continuing as forest clearance continues. Ecology
It is resident in evergreen forest in lowlands and foothills, from 120 m to at least 600 m, particularly hills covered with non-thorny bamboo. It also thrives in a variety of secondary habitats including tall scrub, bamboo, Acacia
, logged evergreen and semi-evergreen forest plantations, perhaps preferring bamboo-covered slopes with a thick leaf-litter layer. Thus it appears to be able to tolerate considerable habitat disturbance and modification. Pairs call in duet. Calling reportedly peaks in March but has been recorded in November in Cambodia. Threats
Extensive deforestation, particularly from herbicide spraying during the Vietnam war, presumably triggered a historic decline. Habitat loss through commercial logging, unofficial timber collection and clearance of land for cultivation (including cashew nut, cassava, rubber and other crop plantations), compounded by high hunting levels across its restricted range, now represent the main threats. Until recently these factors operated in the Cat Loc and Cat Tien protected areas as a result of ineffective management and regulation enforcement, stemming from lack of resources and staff. Illegal forest clearance by settlers has been prevalent in Snoul Wildlife Sanctuary, Cambodia in recent years and 120 km2
of the protected area are in the process of being degazetted to allow further clearance. There is currently extensive legal collection of bamboo in the SBCA, although the impact of this on the species is unknown (Le Manh Hung et al
. 2006). Conservation Actions Underway
In May 1998, a five-year project began in Cat Tien National Park and Cat Loc Nature Reserve (now administratively integrated), focusing on research, developing a conservation management plan, capacity building, community development and conservation education. The Orange-necked Partridge is one of the project's flagship species, and featured on a national stamp in 2000. Extensive surveys have also been carried out in Bu Gia Map National Park (S. Browne in litt.
2004). The known Cambodian population is within the SBCA, a former logging concession which is being managed to promote biodiversity conservation since 2002, primarily by controlling illegal hunting, encroachment and land conversion (Davidson et al.
2003, C. Samnang in litt.
2004, Le Manh Hung et al
. 2006). Snuol Wildlife Sanctuary presumably also holds a population, but receives limited protection, with no external support to the Ministry of Environment (T. Evans in litt.
2007). Following surveys in Binh Phouc Province, Vietnam, the ecological requirements of the species have been refined and recommendations made to extend the boundaries of Bu Gia Map National Park and to create a 'species habitat protection area' for the benefit of Orange-necked Partridge and Germain's Peacock-pheasant Polyplectron germaini
within Nghia Trung and Bu Dang State Forest Enterprises (Le Manh Hung et al
. 2006). Conservation Actions Proposed
Identify and implement management requirements for the species within protected areas in Cambodia and Vietnam. Initiate a conservation education programme for the local people who live around selected protected areas. Quantitatively monitor the populations in Cat Tien and Cat Loc. Conduct surveys for further populations in the largest patches of suitable habitat, such as those in southern Lam Dong, Dong Nai and Binh Duong provinces. Conserve any further sites found to support populations, and follow recommendations to extend the boundaries of Bu Gia Map NP. Continue conservation management improvements in Cat Tien National Park. Carry out ecological studies to determine seasonal habitat use and response to disturbance. Assess the threat posed by hunting to this species and determine what levels of hunting pressure it can withstand. Support the conservation management of SBCA and Snoul Wildlife Sanctuary, Cambodia and Cat Loc, Nam Cat Tien and Bu Gia Map in Vietnam. Survey the Cambodian population to assess its size and global importance. Improve training and resources for forest rangers.
BirdLife International. 2001. Threatened birds of Asia: the BirdLife International Red Data Book. BirdLife International, Cambridge, U.K.
Davidson, P.; Walston, J.; Poole, C. 2002. Endangered partridge discovered in Cambodia. World Birdwatch 24(4): 4.
Davidson, P.; Walston, J.; Poole, C. 2003. Endangered partridge discovered in Cambodia. Newsletter of the Partridge, Quail and Francolin Specialist Group 18: 6-7.
Keane, A.M.; Carroll, J. P.; Fuller, R. A.; McGowan, P.J. K. in press. Partridges, quails, francolins, snowcocks, guineafowl and turkeys: status survey and conservation action plan 2005-2009. IUCN and WPA, Gland, Switzerland.
Le Manh Hung; Nguyen Manh Ha; Tran Thieu Du; Tran Duc Ai; Vuong Duy Lap; Vu Thanh Phong. 2006. The status and distribution of Orange-necked Partridge Arborophila davidi in Binh Phuoc Province, Vietnam.
Nguyen Tran Vy. 2006. Species of Phasianidae in Tan Phu State Forest Enterprise.
Nguyen Xuan Dang; Do Huu Thu; Osborn, T. 2004. A Biological and socio-economic assessment of Da Teh State Forest Enterprise, Lam Dong Province, Vietnam.
Nguyen Xuan Dang; Osborn, T. 2004. Biodiversity and socio-economic assessment of Nghia Trung State Forest Enterprise, Binh Phuoc Province, Vietnam.
Further web sources of information
Alliance for Zero Extinction (AZE) species/site profile. This species has been identified as an AZE trigger due to its IUCN Red List status and limited range.
Detailed species accounts from the Threatened birds of Asia: the BirdLife International Red Data Book (BirdLife International 2001).
Text account compilers
Keane, A., Davidson, P., Bird, J., Harding, M., Benstead, P., Taylor, J.
Browne, S., Evans, T., Pollard, E., Samnang, C., Tordoff, J., Tran Vy, N.
IUCN Red List evaluators
Butchart, S., Symes, A.
BirdLife International (2013) Species factsheet: Arborophila davidi. Downloaded from
http://www.birdlife.org on 21/12/2013.
Recommended citation for factsheets for more than one species: BirdLife International (2013) IUCN Red List for birds. Downloaded from
http://www.birdlife.org on 21/12/2013.
This information is based upon, and updates, the information published in BirdLife International (2000)
Threatened birds of the world. Barcelona and Cambridge, UK: Lynx Edicions and BirdLife International, BirdLife International (2004)
Threatened birds of the world 2004 CD-ROM and BirdLife International (2008) Threatened birds of the world 2008 CD-ROM. These sources provide the information for species accounts for the birds on the IUCN Red List.
To provide new information to update this factsheet or to correct any errors, please email BirdLife
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