This pheasant's small population is naturally fragmented because it lives in small patches of successional grassland. Human population pressure, grazing pressure from livestock, hunting and changing patterns of land-use are resulting in its decline within this habitat, so it qualifies as Vulnerable. Some recent information puts the population size at a lower level than was previously estimated; however, it is not thought likely that all subpopulations are very small, so its status is currently retained as Vulnerable.
del Hoyo, J.; Collar, N. J.; Christie, D. A.; Elliott, A.; Fishpool, L. D. C. 2014. HBW and BirdLife International Illustrated Checklist of the Birds of the World. Barcelona, Spain and Cambridge UK: Lynx Edicions and BirdLife International.
C. wallichii (del Hoyo and Collar 2014) was previously listed as C. wallichi.
Catreus wallichi , Catreus wallichii Sibley and Monroe (1990, 1993), Catreus wallichii Collar and Andrew (1988)
Distribution and populationCatreus wallichii
Male 90-118 cm, female 61-76 cm. Grey, brown and buff bar-tailed pheasant with long crest and red facial skin. Male has largely plain pale-greyish upper neck and clear, dark barring on upperparts. Female is smaller, somewhat duller and more heavily marked. Similar spp. Possibly confusable with female Kalij Pheasant Lophura leucomelanos, but rather pale neck and underparts with dark scaling/mottling rufous-buff to buffish-washed rump, belly and vent, and long, straight barred tail distinctive. Voice Loud chir-a-pir chir-a-pir chir chir-chirwa chirwa and high, piercing chewewoo notes, interspersed with short chut and harsh staccato notes.
occurs in the western Himalayas from north Pakistan
, through Kashmir into Himachal Pradesh and Uttarakhand, India
, and east to central Nepal
(BirdLife International 2001). It has always been reported as uncommon with a patchy distribution owing to its specialised habitat requirements, which often bring it into close proximity to human populations (K. Ramesh in litt.
2004). Many subpopulations are thought to number fewer than ten individuals, living in small pockets of suitable habitat.
In Pakistan, it may now only persist in the Jhelum Valley, where it is declining and has apparently disappeared from some areas (Awan 2011, M. N. Awan in litt.
2013); the most recent surveys found no evidence of it at Salkhala Game Reserve or Machiara National Park where it previously occurred (Awan et al.
In India it has also declined, with most known populations now confined to Himachal Pradesh (where the population was estimated at c.1,000 pairs based on surveys in 1979-1980; S. P. Dhiman in litt.
2013), and Uttarakhand. The area in and around Majathal Wildlife Sanctuary appears to be important with densities of 24 pairs/km2
recorded during 1983 and more recent reports confirming the notion that a sizeable population remains (Subedi 2003), although density estimates of 4-5 pairs/km2
in 2008-1009 suggest that either earlier reported densities were overestimates or the species has undergone a substantial decline (S. P. Dhiman in litt.
2013). The population in the Kai-i-nag area of Kashmir is also thought to be sizeable (R. Kaul in litt.
In Nepal, it appears to be localised, occurring from the Baitadi district in the west, east to the Kali Gandaki River. The most important area in the country is Dhorpatan Hunting Reserve (C. Inskipp and H. S. Baral in litt.
2012). Surveys conducted here in 1981 and 2003 revealed a slight decline, with a corrected population estimate of 127-212 birds in the valley, but this trend was not statistically significant (Subedi 2003). Areas surrounding Dhorpatan have also been found to support populations at similar densities of 5-12.5 birds/km2
, with populations in Surtibhag, Phagune, Bobang and Muri areas estimated at 37 (± 9), 167 (± 16), 67 (± 10) and 101 (±10) pairs respectively and apparently no change in population since surveys in 1981 (Singh et al.
2011). Small populations were identified at Trikuta and within Rara National Park in 2005 and local reports during that survey indicated that the species occurs more widely within Mugu and Jumla districts (Bhudathapa 2006). Surveys in Rara National Park in 2006 and 2008 indicate that the population there is no longer viable, while anecdotal evidence from local shepherds suggests that the species is in decline (Singh 2009) and visiting birdwatchers are finding it more difficult to locate the species (C. Inskipp in litt.
2009). Apparent declines at Ghansa suggest it may have declined overall in Nepal, but the level of threat remains low in parts of its range (Acharya and Thapa 2003); the total Nepalese population is thought likely to number fewer than 1,500 individuals (C. Inskipp and H. S. Baral in litt.
2012). The increasing number of new locations following an increase in survey effort indicates that further areas will be found to support the species in suitable habitat. Population justification
The population was estimated to number 4,000-6,000 individuals, roughly equivalent to 2,700-4,000 mature individuals (R. Kaul in litt.
2007). However, recent surveys of previously surveyed sites in Himachal Pradesh showed evidence of significant declines and even disappearance from some sites, suggesting that a revised population estimate could be 3,000–4,000 individuals (R. Kalsi pers. comm., in Rahmani 2012), roughly equating to 2,000-2,700 mature individuals.Trend justification
This species appears to be particularly vulnerable to hunting pressure as it has a strong association with human settlements, relying on low-level anthropogenic disturbance to maintain its preferred habitat. Hunting pressure and habitat fragmentation are suspected to be causing a moderate global decline.Ecology
It is resident in precipitous, rocky terrain dominated by scrub, tall grass and scattered clumps of trees, most frequently from 1,445-3,050 m, but occasionally down to 950 m at least (Bisht et al.
2007). Occupied sites are characterised by a combination of low shrubs subject to regular browsing and cutting, with grass growing through spring and summer harvested for livestock fodder in the autumn. It has been recorded in regenerating coniferous and broadleaved forests, as well as juniper and rhododendron on grassy slopes (Subedi 2003). Its preference for early successional habitats, often created by traditional grass cutting and burning regimes, has led to an association with human settlements (and therefore high susceptibility to hunting). It digs for roots and tubers, and also eats seeds, berries, insects and grubs (Ali and Ripley 1987). It has been recorded breeding in India in May, June and September with clutch sizes of 6-12 eggs (Bisht et al.
Having been widely shot for sport in the early 20th century, it is still hunted for food and trade, and its eggs are collected for local consumption. Indeed, hunters in Nepal claim that they can trap up to 50 birds in one session through the use of snares and live decoys (Singh 2009), methods that are widespread in the species's range (P. Garson in litt.
2009). Hunting pressure in Nepal may be exacerbated by increased gun-ownership following the Maoist insurgency, especially in the west of the country (C. Inskipp in litt.
2009). The species is hunted in remote areas to provide a traditional treatment of asthma, body pain and fever, and it may be traded locally, although in some areas local people strictly prohibit hunting (C. Inskipp and H. S. Baral in litt.
The patchy nature of its specialised habitat may render the smallest isolated populations vulnerable to extinctions, and higher levels of disturbance, grazing and the felling of wooded ravines now pose a substantial threat. In particular, hunting pressure and habitat destruction by fire and overgrazing have been implicated in its decline in Pakistan (Subedi 2003). However, burning, grazing and timber collection are also important in maintaining moderately disturbed habitats which the species favours, and healthy populations have persisted in some heavily grazed sites such as Chail and Majathal in Himachal Pradesh (P. Garson in litt.
2013), while Singh et al.
(2011) found no significant correlation between pheasant densities with grass cover or measures of grazing pressure in Dhorpatan Valley, Nepal, suggesting that current levels of grazing, timber collection and grass burning were not adversely affecting the species. Conversion of grassland to permanent arable terraces is reducing available habitat, as are schemes to plant mid-altitude grasslands with forest. Nest disturbance by dogs has also been identified as a threat.
Hydroelectric projects (HEPs) have been planned in almost all major rivers and their tributaries in Himachal Pradesh (S. P. Dhiman in litt.
2013). A large area of Majathal Wildlife Sanctuary is under threat from submergence due to the contruction of the Kol Dam upriver on the Satluj River, and large-scale dam projects also threaten sites in the Beas Valley (V. Jolli in litt.
2013). A total of 125 planned HEPs in the major river basins include 43 HEPs in Satluj river basin, 45 in Beas river basin, 26 in Ravi river basin and 11 in Yamuna river basin (S. P. Dhiman in litt.
Many populations in Himachal Pradesh and Uttarakhand lie outside the protected area network and hence are vulnerable to illegal trapping and hunting (R. Kalsi in litt.
2013). Furthermore, in June 2013 the boundaries of many protected areas were redefined to exclude villages, and some important habitats near human habitations (including Majathal, Chail and Kalatop Khajjiar) are now excluded from the protected area network, leaving them at greater risk of development (S. P. Dhiman in litt.
2013). Conservation and Research Actions Underway
CITES Appendix I. The species is legally protected in Nepal and India and occurs in a number of protected areas in those countries. Many status surveys have now been conducted in Himachal Pradesh, principally a week-long intensive survey involving 3,000 Forest Department staff in 2005, which was scheduled for repeat in 2008 (L. Mohan in litt.
2007), in Uttarakhand, India (Bish et al.
2007), and in Nepal using a standardised call count methodology along with research into population ecology and habitat preferences (Subedi 2003, Garson and Baral 2006). Surveys have been undertaken in Rara National Park, mid-western Nepal, in 2006 and 2008 (Singh 2009). An awareness-raising project was carried out in the Kali Gandaki Valley by the Annapurna Conservation Area Project, the World Pheasant Association and Bird Conservation Nepal in 2004. Reintroduction in Pakistan is believed to have been unsuccessful. A workshop was held in Kathmandu in April 2006 to share information gathered in five separate studies within the species's range (Garson and Baral 2006). A captive breeding programme, which aims to build a genetically robust safety net population, is under way in Himachal Pradesh (S. P. Dhiman in litt.
2013).Conservation and Research Actions Proposed
Survey areas where populations have been identified but not yet studied, particularly in western Nepal. Monitor populations at as many key sites as possible, and manage habitat at these sites, using moderate burning and grazing to maintain optimal conditions. Develop a species management plan to cover habitat prescriptions, public awareness and the enforcement of hunting bans. Study burning and grazing regimes at known sites to monitor their impact. Use it as a flagship species in producing and promoting habitat management recommendations based on these studies. Control poaching using legal enforcement and public awareness programmes. Initiate ecotourism projects to generate income at Cheer Pheasant sites (A. Rahmani in litt.
2012). Assess the effects of villagers upon the species and its habitat. Conduct further research into its ecology. Conserve key sites and habitats.
Acharya, B.; Thapa, S. 2003. Preliminary survey of Cheer Pheasant (Catreus wallichi) in lower Kaligandaki valley, Mustang.
Ali, S.; Ripley, S. D. 1987. Compact handbook of the birds of India and Pakistan together with those of Bangladesh, Nepal, Bhutan and Sri Lanka. Oxford University Press, Delhi.
Awan, M. N. 2011. Monitoring and conservation of Cheer Pheasant in Jhelum Catchments, Pakistan. Unpublished final report submitted to the Rufford Small Grants Foundation, UK..
Awan, M. N.; Ali, H.; Lee, D. C. 2012. An annotated checklist of birds and conservation issues in Salkhala Game Reserve, an isolated Important Bird Area in Azad Kashmir, Pakistan. Forktail 28: 38-43.
BirdLife International. 2001. Threatened birds of Asia: the BirdLife International Red Data Book. BirdLife International, Cambridge, U.K.
Bisht, M. S.; Phurailatpam, S.; Kathait, B. S. 2005. Nesting ecology and breeding success of Cheer Pheasant Catreus wallichii in Garhwal Himalaya, India. Journal of the Bombay Natural History Society 102(3): 287-289.
Bisht, M. S.; Phurailatpam, S.; Kathait, B. S.; Dobriyal, A. K.; Chandola-Saklani, A.; Kaul, R. 2007. Survey of threatened Cheer Pheasant Catreus wallichii in Garhwal Himalaya. Journal of the Bombay Natural History Society 104(2): 134-139.
Garson, P.; Baral, H. S. 2006. Cheer Pheasant conservation summit in Kathmandu. Annual Review of the World Pheasant Association 2005/2006: 14-15.
IUCN. 2013. IUCN Red List of Threatened Species (ver. 2013.2). Available at: http://www.iucnredlist.org. (Accessed: 13 November 2013).
Keane, A.M.; Garson, P.J.; McGowan, P.J. K. in press. Pheasants: status survey and conservation action plan 2005-2009. IUCN and WPA, Gland, Switzerland.
Rahmani, A.R. 2012. Threatened Birds of India - Their Conservation Requirements. Oxford University Press.
Singh, P. 2009. Cheer Pheasant in peril in Rara National Park, Nepal. World Pheasant Association News: 4.
Singh, P. B.; Paudel, L.; Sharma, S. 2006. Survey of cheer pheasant Catreus wallichi in and around Dhorpatan Hunting Reserve, Western Nepal.
Singh, P. B.; Subedi, P.; Garson, P. J.; Poudyal, L. 2011. Status, habitat use and threats of cheer pheasant Catreus wallichii in and around Dhorpatan Hunting Reserve, Nepal. International Journal of Galliformes Conservation 2: 22-30.
Subedi, P. 2003. Status and distribution of Cheer Pheasant (Catreus wallichi) in Dhorpatan Hunting Reserve, Nepal.
Further web sources of information
Detailed species accounts from the Threatened birds of Asia: the BirdLife International Red Data Book (BirdLife International 2001).
Explore HBW Alive for further information on this species
Search for photos and videos, and hear sounds of this species from the Internet Bird Collection
Text account compilers
Benstead, P., Bird, J., Davidson, P., Keane, A., Taylor, J., Khwaja, N. & Symes, A.
Acharya, R., Baral, H., Bashir, S., Corder, J., Garson, P., Inskipp, C., Kaul, R., Mohan, L., Ramesh, K., Singh, P., Subedi, P., Rahmani, A., Dhiman, S., Sharma, M., McCausland, I., Jolli, V., Awan, M., Kalsi, R. & Sajwan, K.
BirdLife International (2015) Species factsheet: Catreus wallichii. Downloaded from
http://www.birdlife.org on 30/08/2015.
Recommended citation for factsheets for more than one species: BirdLife International (2015) IUCN Red List for birds. Downloaded from
http://www.birdlife.org on 30/08/2015.
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
To contribute to discussions on the evaluation of the IUCN Red List status of Globally Threatened Birds, please visit BirdLife's Globally Threatened Bird Forums.
Additional resources for this species