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| Subspecies: | Unknown |
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| Est. World Population: | |
| CITES Status: | NOT LISTED |
| IUCN Status: | Critically Endangered |
| U.S. ESA Status: | NOT LISTED |
| Body Length: | |
| Tail Length: | |
| Shoulder Height: | |
| Weight: | |
| Top Speed: | |
| Jumping Ability: | (Horizontal) |
| Life Span: | in the Wild |
| Life Span: | in Captivity |
| Sexual Maturity: | (Females) |
| Sexual Maturity: | (Males) |
| Litter Size: | |
| Gestation Period: | |
Habitat:
It is an extreme lowland specialist, inhabiting primary and well-regenerated, closed canopy, evergreen plains-level forest, below 300 m (Wells 1999, Eaton et al. 2016). The species may have some tolerance of some selective logging (e.g. Johnsgard 1999). However, precise details of its habitat preferences, and its ecological interactions with its congener L. rufa, are lacking. Where L. rufa populations increase (especially on slopes), L. erythrophthalma appears to be excluded and the two species appear to have non-overlapping ranges (Johnsgard 1999, Wells 1999). In Peninsular Malaysia, the species breeds at least during March-September (Wells 1999).
Range:
Lophura erythrophthalma occurs in Peninsular Malaysia, and Sumatra, Indonesia (del Hoyo et al. 1994, Johnsgard 1999). There are just a handful of records from Sumatra, chiefly from Riau and Jambi provinces (van Marle and Voous 1988, eBird 2021). However, it is not a widespread species and appears to be localised, suggesting the total population is moderately small, although it is probably under-recorded owing to its occurrence in less accessible peat forest and karst forest.
Conservation:
Conservation Actions Underway
It occurs in several protected areas, including Taman Negara and Krau Wildlife Reserve (Malaysia). The European captive population is not thought to be currently viable in the long term due to diminishing genetic diversity (A. Hennache in litt. 2004). Conservation Actions Proposed
Advocate full protection under Indonesian and Malaysian law. Conduct further research into its ecological requirements, including its relationship with L. ignita. Conduct extensive field surveys to establish its distribution and population status in Sumatra. Following surveys, review whether key populations are adequately represented within the existing protected areas network, and advocate protection of further areas if necessary. Assist forest managers in habitat identification and zoning of concession areas. Promote the concept of Forest Management Units in Sabah. Develop support mechanisms for key IBAs in Peninsular Malaysia. Promote the careful management of captive stocks including the establishment of a studbook to re-establish a viable captive-breeding programme (Collar and Butchart 2013, R. Wirth in litt. 2022). Continue to closely monitor forest loss using remote sensing data.
It occurs in several protected areas, including Taman Negara and Krau Wildlife Reserve (Malaysia). The European captive population is not thought to be currently viable in the long term due to diminishing genetic diversity (A. Hennache in litt. 2004). Conservation Actions Proposed
Advocate full protection under Indonesian and Malaysian law. Conduct further research into its ecological requirements, including its relationship with L. ignita. Conduct extensive field surveys to establish its distribution and population status in Sumatra. Following surveys, review whether key populations are adequately represented within the existing protected areas network, and advocate protection of further areas if necessary. Assist forest managers in habitat identification and zoning of concession areas. Promote the concept of Forest Management Units in Sabah. Develop support mechanisms for key IBAs in Peninsular Malaysia. Promote the careful management of captive stocks including the establishment of a studbook to re-establish a viable captive-breeding programme (Collar and Butchart 2013, R. Wirth in litt. 2022). Continue to closely monitor forest loss using remote sensing data.




