Nisaetus nanus

Taxonomy

Assessment Information

Geographic Range

Population

Habitat and Ecology

Threats

Conservation Actions

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Taxonomy [top]

Kingdom	Phylum	Class	Order	Family
ANIMALIA	CHORDATA	AVES	FALCONIFORMES	ACCIPITRIDAE

Scientific Name:

Nisaetus nanus

Species Authority:

(Wallace, 1868)

Common Name/s:

English	–	Wallace's Hawk-eagle, Wallace's Hawk-Eagle
Spanish	–	Aguila-azor de Wallace

Taxonomic Notes:

Spizaetus nanus, S. lanceolatus, S. philippensis, S. pinskeri, S. nipalensis, S. alboniger and S. bartelsi (Sibley and Monroe 1990, 1993) and S. cirrhatus and S. floris (Gjershaug et al. 2004) have been transferred into the genus Nisaetus following Haring et al. (2006). S. africanus and Hieraaetus fasciatus (Sibley and Monroe 1990, 1993) have both been transferred into Aquila, also following Haring et al. (2006); and H. kienerii (Sibley and Monroe 1990, 1993) has been transferred into the resurrected genus Lophotriorchis. The BirdLife Taxonomic Working Group is aware that phylogenetic analyses have been published which have proposed moving H. pennatus into Aquila but as not all published studies are concordant we prefer not to take a decision on this until cladogenesis of the 'booted eagles' has been resolved.

Assessment Information [top]

Red List Category & Criteria:

Vulnerable A2c+3c+4c ver 3.1

Year Published:

2012

Assessor/s:

BirdLife International

Reviewer/s:

Butchart, S. & Symes, A.

Contributor/s:

Aik, Y., Davison, G. & Iqbal, M.

Justification:
This species is suspected to be undergoing a rapid population decline owing to the widespread and on-going loss of lowland forest, which qualifies it as Vulnerable.

History:

2008	–	Vulnerable
2004	–	Vulnerable
2000	–	Vulnerable
1996	–	Vulnerable
1994	–	Vulnerable

Geographic Range [top]

Range Description:	Spizaetus nanus occurs in southern Tenasserim, Myanmar, peninsular Thailand, Peninsular and East (Sabah and Sarawak) Malaysia, Brunei, and Kalimantan and Sumatra, Indonesia (BirdLife International 2001). Although still widespread, it is uncommon or rare throughout its range. It may be nearing extinction in Thailand and is declining everywhere. However, its status is somewhat unclear because of the difficulties of separating it from S. alboniger.
Countries:	Native: Brunei Darussalam; Indonesia; Malaysia; Myanmar; Thailand
Range Map:	Click here to open the map viewer and explore range.

Population [top]

Population:	The population size is preliminarily estimated to fall into the band 2,500-9,999 mature individuals. This equates to 3,750-14,999 individuals in total, rounded here to 3,500-15,000 individuals.
Population Trend:	Decreasing

Habitat and Ecology [top]

Habitat and Ecology:	It is resident in evergreen forests, chiefly in the lowlands and on lower hill-slopes, but has occasionally been reported up to 1,000 m. It may tolerate some habitat degradation, having been recorded in heavily logged forest in Kalimantan and Sumatra, and logged forest in Malaysia. However, a study in Malaysia recorded it in primary forest prior to selective logging, but not subsequently.
Systems:	Terrestrial

Threats [top]

Major Threat(s):	The key threats are habitat loss, degradation and fragmentation as a result of large-scale commercial logging, including within protected areas, and widespread forest clearance for plantation agriculture (primarily rubber and oil-palms). Between 1985-1997, nine million and nearly seven million hectares of forest were lost on Kalimantan and Sumatra, respectively. The impact of the major fires of 1997-1998 has yet to be fully assessed, but fires appear to be increasing in frequency and severity on Sumatra and Borneo. In Thailand, virtually all lowland forest has now been cleared, and encroachment continues on the lower slopes of almost all mountains. Despite these negative statistics, the species has shown resilience to at least a degree of habitat modification, even recorded within small lowland forest patches within oil palm plantations in Sabah (Yeap Chin Aik in litt. 2007).

Major Threat(s):

The key threats are habitat loss, degradation and fragmentation as a result of large-scale commercial logging, including within protected areas, and widespread forest clearance for plantation agriculture (primarily rubber and oil-palms). Between 1985-1997, nine million and nearly seven million hectares of forest were lost on Kalimantan and Sumatra, respectively. The impact of the major fires of 1997-1998 has yet to be fully assessed, but fires appear to be increasing in frequency and severity on Sumatra and Borneo. In Thailand, virtually all lowland forest has now been cleared, and encroachment continues on the lower slopes of almost all mountains. Despite these negative statistics, the species has shown resilience to at least a degree of habitat modification, even recorded within small lowland forest patches within oil palm plantations in Sabah (Yeap Chin Aik in litt. 2007).

Conservation Actions [top]

Conservation Actions:	Conservation Actions Underway CITES Appendix II. It occurs in numerous protected areas, including at least six (four national parks and two wildlife reserves) on Sumatra, at least three (two national parks and one wildlife reserve) in Kalimantan, at least five (one national park and four wildlife sanctuaries) in Thailand, at least three (two national parks and one wildlife reserve) in Malaysia, and one wildlife sanctuary in Myanmar. Conservation Actions Proposed Conduct extensive surveys to more clearly establish its distribution and status compared with S. alboniger. Conduct research into its ecological requirements, particularly its tolerance of habitat degradation and its ranging behaviour. Promote the concept of Forest Management Units in Sabah. Assist forest managers in habitat identification and zoning of concession areas. Afford it full legal protection under Myanmar, Thai, Indonesian and Malaysian law.

Conservation Actions:

Conservation Actions Underway
CITES Appendix II. It occurs in numerous protected areas, including at least six (four national parks and two wildlife reserves) on Sumatra, at least three (two national parks and one wildlife reserve) in Kalimantan, at least five (one national park and four wildlife sanctuaries) in Thailand, at least three (two national parks and one wildlife reserve) in Malaysia, and one wildlife sanctuary in Myanmar.

Conservation Actions Proposed
Conduct extensive surveys to more clearly establish its distribution and status compared with S. alboniger. Conduct research into its ecological requirements, particularly its tolerance of habitat degradation and its ranging behaviour. Promote the concept of Forest Management Units in Sabah. Assist forest managers in habitat identification and zoning of concession areas. Afford it full legal protection under Myanmar, Thai, Indonesian and Malaysian law.

Citation:	BirdLife International 2012. Nisaetus nanus. In: IUCN 2012. IUCN Red List of Threatened Species. Version 2012.2. <www.iucnredlist.org>. Downloaded on 25 May 2013.
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