||Grey-banded Mannikin, Grey-banded Munia
||del Hoyo, J., Collar, N.J., Christie, D.A., Elliott, A., Fishpool, L.D.C., Boesman, P. and Kirwan, G.M. 2016. HBW and BirdLife International Illustrated Checklist of the Birds of the World. Volume 2: Passerines. Lynx Edicions and BirdLife International, Barcelona, Spain and Cambridge, UK.
||10 cm. Pale-headed munia. Grey head, brownish-grey breast, narrow, grey lower breast-band, rufous-brown belly, dark brown mantle and wings, and pale yellow rump and tail. Similar spp. Other pale-headed munias elsewhere in New Guinea have different pattern to underparts. On Vogelkop, Streak-headed Munia L. tristissima is all dark except for yellowish rump and uppertail-coverts, and inhabits lowland forest edge. Voice High, thin ts ts ts ... Hints Search wet grasslands and different agricultural crops beside Anggi Gigi.
|Red List Category & Criteria:
||Butchart, S. & Symes, A.
||Bishop, K., Bostock, N. & Gibbs, D.
||Benstead, P., Gilroy, J., Taylor, J.
This little-known species is only known from one location, qualifying it as Vulnerable. If it proves to be declining, for instance through agricultural conversion of its naturally scarce and fragmented habitat, then it would be reclassified as Critically Endangered, but further research may show it to occur at other sites in this very poorly known area.
|Previously published Red List assessments:|
- 2012 – Vulnerable (VU)
- 2008 – Vulnerable (VU)
- 2004 – Vulnerable (VU)
- 2000 – Vulnerable (VU)
- 1996 – Vulnerable (VU)
- 1994 – Vulnerable (VU)
- 1988 – Lower Risk/least concern (LR/lc)
|Range Description:||Lonchura vana is endemic to the Arfak Mountains in the Vogelkop Peninsula in north-west Papua (formerly Irian Jaya), Indonesia (Hoogerwerf 1971, Beehler et al. 1986). It is poorly known, but could be restricted to a single location - grasslands around the lake Anggi Gigi (D. Gibbs in litt. 2000). Other reports that it occurs elsewhere in the Arfaks, such as the Tamrau Mountains (Hoogerwerf 1971, Beehler et al. 1986) appear to be unsubstantiated, and there are no records from around the neighbouring lake, Anggi Gite. Its possible occurrence elsewhere is limited by the scarcity of its habitat (N. Bostock in litt. 1993, D. Gibbs in litt. 1994). However, the Arfaks have not been well-explored and it may prove to occur elsewhere (K. D. Bishop in litt. 2000). |
|♦ Continuing decline in area of occupancy (AOO):||Unknown|
|♦ Extreme fluctuations in area of occupancy (AOO):||No||♦ Estimated extent of occurrence (EOO) - km2:||550|
|♦ Continuing decline in extent of occurrence (EOO):||Unknown||♦ Extreme fluctuations in extent of occurrence (EOO):||No|
|♦ Number of Locations:||1||♦ Continuing decline in number of locations:||Unknown|
|♦ Extreme fluctuations in the number of locations:||No||♦ Lower elevation limit (metres):||1900|
|♦ Upper elevation limit (metres):||2000|
|Range Map:||Click here to open the map viewer and explore range.|
|Population:||The global population is estimated to number no more than 10,000 individuals, and so it is placed in the band 2,500-9,999 individuals. This equates to 1,667-6,666 mature individuals, rounded here to 1,500-7,000 mature individuals.|
Trend Justification: There is insufficient information to infer population trends for this species. However, there is no evidence of any factors currently threatening the population, so it is suspected to be stable.
|Current Population Trend:||Stable|
|♦ Number of mature individuals:||1500-7000||♦ Continuing decline of mature individuals:||Unknown|
|♦ Extreme fluctuations:||No||♦ Population severely fragmented:||No|
|♦ No. of subpopulations:||1||♦ Continuing decline in subpopulations:||Unknown|
|♦ Extreme fluctuations in subpopulations:||No||♦ All individuals in one subpopulation:||Yes|
|♦ No. of individuals in largest subpopulation:||100|