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| Subspecies: | Unknown |
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| Est. World Population: | |
| CITES Status: | NOT LISTED |
| IUCN Status: | Vulnerable |
| U.S. ESA Status: | NOT LISTED |
| Body Length: | |
| Tail Length: | |
| Shoulder Height: | |
| Weight: | |
| Top Speed: | |
| Jumping Ability: | (Horizontal) |
| Life Span: | in the Wild |
| Life Span: | in Captivity |
| Sexual Maturity: | (Females) |
| Sexual Maturity: | (Males) |
| Litter Size: | |
| Gestation Period: | |
Habitat:
Habitat requirements for Dugongs include coastal areas, shallow to medium deep, warm waters (15-17°C minimum with behavioural thermoregulation), seagrass beds supporting sub-tropical and tropical species of seagrass, particularly low fiber species (Hines et al. 2012, Marsh et al. 2011). Dugongs show great variability in movement patterns and migration, depending on the study area and the influence of seasonal temperature or rainfall on regional ecosystems. Long-distance movements by Dugongs along the Queensland coast are well-documented (Sheppard et al. 2006), even though Dugongs do not appear to undertake regular migrations and individual movements are individualistic (Sheppard et al. 2006, Marsh et al. 2011, Gredzens et al. 2014). Cope et al. (2015) used pedigree analysis based on individual genetic markers to infer the movements of Dugongs between locations in southeast Queensland including Moreton Bay and Hervey Bay. They found that approximately 30% of assigned parents had at least one offspring found in a different locality, implying recent movement of the parent or offspring. This analysis suggested markedly more movement between localities than detected through repeated direct sampling of individuals (Seddon et al. 2014) or through telemetry (Sheppard et al. 2006).
Range:
Dugongs inhabit coastal and island waters between East Africa and Vanuatu between latitudes of about 27° north and south of Equator. Spanning approximately 128,000 km of coastline (860,000 km2) across at least 37 and and possibly occur in an additional seven states and territories (Marsh et al. 2011, N. Pilcher pers. comm).
Conservation:
Dugongs are covered under three international conservation conventions: The Convention on Biological Diversity (CBD), the Convention on the International Trade in Endangered Species of Wild Fauna and Flora (CITES) and the Convention on Migratory Species of Wild Animals (also known as CMS or the Bonn Convention). Dugongs are also included in the Coral Triangle Initiative (CTI), goal five (Threatened Species). Additionally, the Convention on Wetlands (the Ramsar Convention) protects some important Dugong habitats.
To date, there has been little effective management intervention to reduce anthropogenic impacts on the Dugong, apart from legislative protection which is almost ubiquitous throughout its range. Protected area initiatives aim to protect Dugongs in many range states (Marsh et al. 2011) and are most developed in Australia. Most of the marine protected areas outside Australia with the potential to protect Dugongs are ‘paper parks’ where laws and regulations exist but are not implemented. Strategic Action Programmes/Strategic Plans/Action Plans to protect Dugongs have been developed by countries in the Red Sea and Gulf of Aden region (Gerges 2002), Indonesia (de Iongh et al. 2009a, 2009b) and South Pacific Regional Environmental Programme (SPREP; Gillespies 2005). However, effective enforcement of conservation regulations is a problem throughout most of the region because of poverty, lack of resources and personnel. The most pressing need is for alternative sustainable livelihoods that address poverty and provide incentives for conservation. The most promising initiative is the UNEP Dugong, Seagrass & Coastal Communities Initiative (see http://www.cms.int/en/publication/dugong-seagrass-and-coastal-communities-initiative).
To date, there has been little effective management intervention to reduce anthropogenic impacts on the Dugong, apart from legislative protection which is almost ubiquitous throughout its range. Protected area initiatives aim to protect Dugongs in many range states (Marsh et al. 2011) and are most developed in Australia. Most of the marine protected areas outside Australia with the potential to protect Dugongs are ‘paper parks’ where laws and regulations exist but are not implemented. Strategic Action Programmes/Strategic Plans/Action Plans to protect Dugongs have been developed by countries in the Red Sea and Gulf of Aden region (Gerges 2002), Indonesia (de Iongh et al. 2009a, 2009b) and South Pacific Regional Environmental Programme (SPREP; Gillespies 2005). However, effective enforcement of conservation regulations is a problem throughout most of the region because of poverty, lack of resources and personnel. The most pressing need is for alternative sustainable livelihoods that address poverty and provide incentives for conservation. The most promising initiative is the UNEP Dugong, Seagrass & Coastal Communities Initiative (see http://www.cms.int/en/publication/dugong-seagrass-and-coastal-communities-initiative).




