|Scientific Name:||Todiramphus australasia (Vieillot, 1818)|
Halcyon australasia australasia Collar and Andrew (1988)
Todirhamphus australasia australasia Sibley and Monroe (1990, 1993)
Todirhamphus australasia australasia Collar et al. (1994)
|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. Volume 1: Non-passerines. Lynx Edicions BirdLife International, Barcelona, Spain and Cambridge, UK.|
|Red List Category & Criteria:||Near Threatened ver 3.1|
|Reviewer(s):||Butchart, S. & Symes, A.|
|Facilitator/Compiler(s):||Benstead, P., Gilroy, J., Khwaja, N., Taylor, J., Westrip, J.|
This species is listed as Near Threatened as it is currently considered to have a moderately small and fragmented population which is likely to be declining owing to habitat loss. A re-assessment of the potential population size may mean that the species warrants downlisting in the future.
|Previously published Red List assessments:|
|Range Description:||Todiramphus australasia is restricted to four Endemic Bird Areas (Northern Nusa Tenggara, Sumba, Timor and Wetar, and the Banda Sea Islands, the first three with nominate australasia, the last one with subspecies dammeriana and odites), in Indonesia and Timor-Leste. Its distribution within this fairly wide area is, however, very patchy, and it is generally uncommon, although a recent visit to Wetar found the species to be widespread, occurring at all forest sites (Trainor et al. 2009).|
|Range Map:||Click here to open the map viewer and explore range.|
|Population:||The population size of this species has not been quantified, but it has been described as generally uncommon, and it does maintain healthy populations in many areas (see Trainor and Verbelen 2013).|
Trend Justification: Data on trends are lacking, but a slow to moderate decline is suspected to have occurred as this species depends on closed-canopy forest, which has been affected by development and logging within its range.
|Current Population Trend:||Decreasing|
|Habitat and Ecology:||This species is a closed-canopy specialist, occurring in monsoon forest at 0-700 m. It is also found in secondary habitats, such as gardens and cultivated areas, provided that sufficient canopy cover remains.|
|Continuing decline in area, extent and/or quality of habitat:||Yes|
|Generation Length (years):||4.8|
|Movement patterns:||Not a Migrant|
Habitat loss and degradation seem likely to be considerable negative factors. On Wetar, pressure comes from agriculture, logging, mining and road-building, although much of the island is inaccessible (Trainor et al. 2009).
Conservation Actions Underway
None are known.
Conservation Actions Proposed
Monitor populations across its range to determine whether declines are occurring. Conduct ecological studies to determine its habitat requirements and tolerance of secondary habitats. Effectively protect significant areas of suitable forest at key sites, in both strictly protected areas and community-led multiple use areas.
|Amended reason:||Edited Rationale and Population Trend Justification. Added a reference and a Facilitator/Compiler.|
|Citation:||BirdLife International. 2017. Todiramphus australasia (amended version of 2016 assessment). The IUCN Red List of Threatened Species 2017: e.T22683428A117223872.Downloaded on 23 May 2018.|
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