|Scientific Name:||Chlamydosaurus kingii|
|Species Authority:||Gray, 1825|
|Taxonomic Notes:||This is the sole member of its genus.|
|Red List Category & Criteria:||Least Concern ver 3.1|
|Assessor(s):||Doughty, P. & Allison, A.|
|Reviewer(s):||Böhm, M., Collen, B. & Ram, M. (Sampled Red List Index Coordinating Team)|
|Contributor(s):||De Silva, R., Milligan, H.T., Wearn, O.R., Wren, S., Zamin, T., Sears, J., Wilson, P., Lewis, S., Lintott, P. & Powney, G.|
Chlamydosaurus kingii has been assessed as Least Concern owing to its large distribution. There are a number of localized threats causing small population declines, however, these are not impacting over large parts of this species' range. Monitoring should continue as an increase in threat levels and therefore population decline will trigger a threat category in the future.
|Range Description:||This lizard is distributed in a band across northern Australia, from the Kimberley district, Western Australia, through northern Northern Territory, to Cape York Peninsula and eastern Queensland. It also occurs in southern New Guinea.|
Native:Australia; Papua New Guinea
|Range Map:||Click here to open the map viewer and explore range.|
|Population:||There is no population information for this species.|
|Current Population Trend:||Unknown|
|Habitat and Ecology:||This is an arboreal and diurnal lizard, occurring in dry sclerophyll forests and woodlands (Cogger 2000).|
|Use and Trade:||Many individuals are collected from the wild, but it is unknown whether this species can be bred in captivity.|
|Major Threat(s):||Various threats are likely to be causing declines in this species. Late dry season fires in the Northern Territory were responsible for an approximate 30% mortality rate in a small monitored population in Kakadu National Park, though no mortality was recorded in the early dry season fires (Griffiths 1994). Local population declines have also been reported after the arrival of the cane toad, Rhinella marina (Breeden 1963). Predation by cats has also caused declines in this species (Brook et al. 2004). In the Trans-Fly region of New Guinea, this species is reported to be "highly sought after for the pet trade" (Allison 2006).|
|Conservation Actions:||This species occurs in Kakadu National Park, and is likely to occur in others. Localized populations of this species are monitored to study the impact that major threats such as fire are having on its population abundance. Population monitoring should be extended to other populations, and research into its harvest levels should be carried out.|
Allison, A. 2006. Reptiles and Amphibians of the Trans-Fly Region of New Guinea. Pacific Biological Survey, Bishop Museum, WWF South Pacific Programme.
Allison, A. 2007. pers. comm. Red List Assessment.
Breeden, K. 1963. Cane Toad (Bufo marinus). Wildlife in Australia 1: 31.
Brook, B.W., Whitehead, P.J. and Dingle, J.K. 2004. Potential cane toad short to medium term control techniques - the biological feasibility and cost of exclusion as a mitigating control strategy. Final report for the Australian government department of the environment and heritage. Key centre for tropical wildlife management, Charles Darwin University.
Cogger, H.G. 2000. Reptiles and Amphibians of Australia. New Holland Publishers, Sydney.
Doughty, P. 2007. pers. comm. Red List Assessment.
Griffiths, T. 1994. The short-term effects of fire on frillneck lizards in the Top End. In: D.B. Rose (ed.) (ed.), Country in Flames: Biodiversity and Fire in North Australia. Darwin.
IUCN. 2010. IUCN Red List of Threatened Species (ver. 2010.4). Available at: http://www.iucnredlist.org. (Accessed: 27 October 2010).
|Citation:||Doughty, P. & Allison, A. 2010. Chlamydosaurus kingii. The IUCN Red List of Threatened Species 2010: e.T170384A6773533.Downloaded on 30 April 2017.|
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