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Southern Cassowary Casuariuscasuarius
This species is believed to have undergone a rapid decline in the last three generations (44 years) in Australia, and declines of a similar magnitude elsewhere in its range are possible, with local extirpations reported from parts of New Guinea. It is therefore classified as Vulnerable. However, the decline in Australia resulted from an extraordinary rate of habitat destruction which has virtually ceased. E. 2008. Systematics and taxonomy of Australian birds. J.; Christie, D. A.; Elliott, A.; Fishpool, L. D. C. 2014. HBW and BirdLife International Illustrated Checklist of the Birds of the World. Barcelona, Spain and Cambridge UK: Lynx Edicions and BirdLife International.180 cm. Very large, black ratite. Adult black with bright blue neck. Red on lower nape. Red double wattle hanging from foreneck. Similar spp. Larger than Dwarf Cassowary C. bennetti and adult has high casque and double red wattle. Voice Booming display call and various rumblings and hissings, usually given when disturbed. Chicks make frequent, high pitched and frequency modulated whistles as contact calls to male. It occurs throughout the lowlands of New Guinea except for the northern watershed from the Vogelkop to the Huon Peninsula (Coates 1985, Beehler et al. 1986). In Papua and adjacent islands, its status is unclear, but it may be more common than in Papua New Guinea. In Papua New Guinea, it has declined, and is now absent in some locations, including remote areas (Coates 1985, K. D. Bishop in litt. 1999). In Australia, there are 3 subpopulations in Queensland. The southern and largest population ranges from the Paluma Range north of Townsville to Mt Amos. Two populations occur further north on Cape York Peninsula: one in the McIlwraith Range and north to the Pascoe River, the other in the Jardine River National Park and Heathland Resources Reserve (Kofron and Chapman 2006). The Australian population was estimated to number c. 2,500 birds in 2010, but it is declining (Garnett et al. Garnett et al. (2011) estimated the Australian population to number 2,500 mature individuals. Its diet largely comprises fallen wholesale nba jerseys china fruit, although it is fairly undiscriminating (Garnett et al. 2011). It ranges between 0 m and at least 500 m in Papua New Guinea (Johnson et al. In Indonesia and Papua New Guinea, the species is heavily hunted, captured and traded close to populated areas, being of high cultural importance, and constituting a major food source for subsistence communities (Coates 1985, Beehler et al. 1986, K. D. Bishop in litt. 1999). This hunting and trade is not sustainable in many areas and has led to its extirpation from some sites, as the species is traded at a sub national level to supply markets in more densely populated areas (Johnson et al. 2004). Increasing human populations and the spread of shotguns used for hunting exacerbate hunting pressure on the species. However, although birds appear to be more common in unpopulated areas (Beehler et al. 1994, Burrows 1995), they can apparently survive in some hunted areas (Beehler 1985), probably those where traditional hunting techniques predominate. Industrial logging is threatening large areas of suitable habitat in New Guinea, with unknown but potentially significant impact on the species, and clearance for oil palm plantations is a significant wholesale nhl jerseys but unquantified threat. Cyclones are considered a threat to the species in Australia, with cyclones severely affecting Cassowary habitat in 2006 and 2011. In 2006, Cyclone Larry hit Queensland, affecting fruit production in tropical rain forests and causing the death of some cassowaries, either directly or as a result of starvation and exposure to other threats following the cyclone. In addition, following the cyclone some individuals could have ventured beyond forest fragments and may have suffered higher mortality through collisions with motor vehicles or attacks by dogs (L. A. Moore N. J. Moore unpub. data to Bellingham 2008). tuberculosis) following such events may pose a threat to the species (Cooper 2008), although this is yet to be confirmed. Climate change could increase the severity of cyclones in the future. It should be noted, however, that even large cyclones have a severe effect on only a small proportion of cassowary habitat.Conservation Actions UnderwayA recovery plan for the species in Australia was published in 2002 (Queensland Parks and Wildlife Service 2002) and updated in cheap jerseys 2007 (Latch 2007). In Australia, programmes have been aimed at community education, localised habitat management, protection wholesale jerseys and revegetation, management plans for populations and high risk individuals, surveys, survey and translocation methods, and habitat use. Temporary feeding stations have been installed in damaged areas following cyclones in Australia. Most remaining habitat is within protected areas (Westcott 1999, D. Westcott in litt. 1999, Garnett et al. 2011). A village based survey has been conducted in Papua New Guinea investigating sustainability of wildlife capture and trade (Johnson et al. 2004). Conservation Actions ProposedQuantify forest loss in New Guinea. Determine population densities, sizes and demographic trends throughout its range. In Indonesia and Papua New Guinea: Monitor populations in protected areas. Quantify the effects of hunting and logging. Promote community based hunting restrictions. In Australia: Revise monitoring techniques and monitor key sites. Research population dynamics. Research impact of cyclones, dogs, traffic, disease and fragmentation on persistence of small populations and on survivorship and demography. Prevent habitat clearance. Minimise cassowary road deaths and dog attacks, and assess impact of pigs. Undertake dog and pig control areas of in dense populations (Garnett et al. 2011). Investigate the feasibility and merits and, if appropriate, implement a translocation plan as part of rescue, rehabilitation and release. Identify areas and corridors to protect, restore, manage, develop and implement Cassowary Conservation Local Area Plans as part of local planningBeehler, B. 1985. Conservation of New Guinea rainforest birds. (ed.), Conservation of tropical forest birds, pp. 233 247.Beehler, B. M.; Burg, C. G.; Filardi, C.; Merg, K. 1994. Birds of the Lakekamu Kunamaipa Basin. Muruk 6(3): 1 8.Beehler, B. M.; Pratt, T. K.; Zimmerman, D. A. 1986. Birds of New Guinea. Princeton University Press, Princeton.Bellingham, P. J. 2008. Cyclone Effects on Australian Rain Forests: An Overview. Austral 33(4): 580 584.Burrows, I. 1995. A field survey of the avifauna of the Kikori river basin.Johnson, A.; Bino, R.; Igag, P. 2004. A preliminary evaluation of the sustainability of cassowary (Aves: Casuariidae) capture and trade in Papua New Guinea. Animal Conservation 7(2): 129 137.Kofron, C. P.; Chapman, A. 2006. Causes of mortality to the endangered Southern Cassowary Casuarius casuarius johnsonii in Queensland, Australia. Pacific Conservation Biology 12(3): 175 179.Articles Connexes：