|Scientific Name:||Argusianus argus|
|Species Authority:||(Linnaeus, 1766)|
|Taxonomic Source(s):||del Hoyo, J., Collar, N.J., Christie, D.A., Elliott, A. and Fishpool, L.D.C. 2014. HBW and BirdLife International Illustrated Checklist of the Birds of the World. Lynx Edicions BirdLife International.|
|Taxonomic Notes:||A. bipunctactus is no longer accepted as a valid species by the BirdLife Taxonomic Working Group, based on the evidence presented in Davison & McGowan (2009). It is treated here as a synonym of A. argus.|
|Red List Category & Criteria:||Near Threatened ver 3.1|
|Facilitator/Compiler(s):||Benstead, P., Mahood, S., Taylor, J.|
This spectacular pheasant is undoubtedly suffering from the twin threats of habitat loss and hunting throughout its extensive range. It is probably undergoing a moderately rapid population reduction and is consequently classified as Near Threatened.
|Previously published Red List assessments:||
|Range Description:||Argusianus argus is confined to the Sundaic lowlands, where it is recorded from south Tenasserim, Myanmar, peninsular and south-west Thailand, Sabah, Sarawak and Peninsular Malaysia, Brunei (extirpated from many areas), Kalimantan and Sumatra, Indonesia (BirdLife International 2001). It is generally uncommon, although this species has probably not declined very rapidly because it ranges up to elevations where forest loss is less severe and occurs it in selectively logged sites. Densities recorded in south-western Sumatra ranged from 0.9 to 3.7 birds/km2 (Winarni et al. 2009).|
Native:Brunei Darussalam; Indonesia; Malaysia; Myanmar; Thailand
|Continuing decline in area of occupancy (AOO):||Unknown|
|Extreme fluctuations in area of occupancy (AOO):||No|
|Estimated extent of occurrence (EOO) - km2:||1350000|
|Continuing decline in extent of occurrence (EOO):||Unknown|
|Extreme fluctuations in extent of occurrence (EOO):||No|
|Continuing decline in number of locations:||Unknown|
|Extreme fluctuations in the number of locations:||No|
|Upper elevation limit (metres):||1500|
|Range Map:||Click here to open the map viewer and explore range.|
|Population:||The total population is estimated to number more than 100,000 individuals.
Trend Justification: There are no data on population trends; however, the species is suspected to be in decline at a moderately rapid rate, owing to hunting and habitat loss.
|Current Population Trend:||Decreasing|
|Habitat and Ecology:||It occurs in tall, dry, lowland primary, secondary and logged forests, up to 1,300 m, but principally, below 900 m (BirdLife International 2001, Dinata et al. 2008). It is much sparser in deciduous forest and rare to absent from lowland peat swamp and white-sand heath forests. A recent study in Sumatra, utilising radio-tracking, habitat sampling, camera trapping and transect surveys found that territories averaged 14.5 ha, used mostly by resident males, who showed a preference for undisturbed forest (Winarni et al. 2009). Both sexes show a preference for intact forest with large trees and an open understorey. The species's diet includes fruits, seeds, flowers, leaf buds and invertebrates (Winarni et al. 2009).|
|Continuing decline in area, extent and/or quality of habitat:||Unknown|
|Generation Length (years):||5.4|
|Movement patterns:||Not a Migrant|
Forest destruction in the Sundaic lowlands of Indonesia and Malaysia has been extensive (Kalimantan lost nearly 25% of its evergreen forest during 1985-1997, and Sumatra lost almost 30% of its 1985 cover), because of a variety of factors, including the escalation of logging and land conversion, with deliberate targeting of all remaining stands of valuable timber including those inside protected areas, plus forest fires (particularly in 1997-1998). At present, less than 13% of Sumatra's original lowland forest cover remains (Winarni et al. 2009). Declines are compounded by trapping for the cage-bird industry. However, the species's use of secondary growth and higher elevations implies that it is not immediately threatened. The impacts of anthropogenic threats may be compounded by pressures from drought events, such as those linked to the El Niño Southern Oscillation (ENSO) (Winarni et al. 2009).
Conservation Actions Underway
CITES Appendix II. Conservation Actions Proposed
Survey to assess the size of the population. Regularly monitor the population at selected sites. Asses the effect of hunting both inside and outside protected areas. Conduct local education programmes to discourage hunting. Enforce the protection afforded to the species's habitat through protected areas and protect additional large areas of forest in areas where it occurs.
|Citation:||BirdLife International. 2013. Argusianus argus. The IUCN Red List of Threatened Species 2013: e.T22725006A50438075. . Downloaded on 25 May 2016.|
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