Size in Square Kilometres
Qualifying Species and Criteria
Dugong – Dugong dugon
Criterion A; B (1); C (2)
Australian snubfin dolphin – Orcaella heinsohni
Criterion A; B (1); C (2); D (1)
Australian humpback dolphin – Sousa sahulensis
Criterion A; B (1); C (2)
Indo-Pacific bottlenose dolphin – Tursiops aduncus
Criterion B (1); C (2)
Marine Mammal Diversity
Megaptera novaeangliae, Stenella longirostris, Pseudorca crassidens, Orcinus orca, Balaenoptera musculus brevicauda
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The boundary of this IMMA aligns with the network of Biologically Important Areas identified by the Australian Commonwealth for the dugong (Dugong dugon) and Australian snubfin dolphin (Sousa sahulensis) across the northwest of Australia and extends out to the 50m contour from Gourdon Bay in the south, encompassing the complex coastline and inland waters of the Kimberley coastline to the border with the Northern Territory in the north. The tropical Kimberley region of northern Western Australia is well known for its outstanding natural features, vast and remote landscapes and Indigenous cultural significance. The inshore marine environment has rugged and dynamic coastline, characterised by tidal movements of up to 10 metres, form extensive intertidal habitats adjacent to rocky shores and headlands, islands, sandy beaches and tidal rivers. This physically complex inshore environment supports a diverse range of habitats including seagrass, coral reefs, extensive intertidal mudflats and sponge-dominated filter-feeding communities with high levels of biological diversity. The importance of this region has been recognised through the creation of a network of State and Commonwealth marine protected areas that are jointly managed with traditional owners, stretching from Eighty Mile Beach Marine Park, Yawuru Nagulugan Roebuck Bay Marine Park, Lalang garram/Camden Sound and Horizontal Falls Marine Parks, and North Kimberley Marine Park. Eleven Aboriginal communities have saltwater country across this stretch of coastline, many with their own healthy country or indigenous protected area plans identifying cultural values, significance and ecological knowledge (e.g. Bardi Jawi Indigenous Protected Area Management Plan, Yawuru Cultural Plan, Dambimangari Healthy Country Plan, Wunambal Gaambera Healthy Country Plan, Balangarra Healthy Country Plan, Mayala Healthy Country Plan, Karajarri Healthy Country Plan). Some of these identify spatial areas of importance to marine mammals while others note the cultural importance of species.
The species that are relevant to this IMMA include the Australian snubfin dolphin (Orcaella heinsohni), Australian humpback dolphin (Sousa sahulensis) (both endemic to northern Australia), Indo-Pacific bottlenose dolphin (Tursiops aduncus) and dugong (Dugong dugon), dwarf spinner dolphin (Stenella longirostris roseiventris), humpback whale (Megaptera novaeangliae), killer whale (Orcinus orca), false killer whale (Pseudorca crassidens) and pygmy blue whale (Balaenoptera musculus brevicauda). While the humpback whale is seasonally present during the migration season, using coastal waters for breeding and resting areas, other species are considered regular or occasional visitors to the region. Dugongs are present throughout the Kimberley coastal region, in strong association with seagrass habitat. While there is a significant population of dugongs across the Kimberley, little is known about their movement patterns, connectivity between areas and size of their foraging range. Some seasonal patterns of movement have been detected using satellite tags (Campbell et al 2010) and confirmed from traditional ecological knowledge. A number of hotspot areas for dugongs were identified across the Kimberley based on a recent aerial survey, combined with predictive seagrass habitat mapping, indigenous knowledge and previous surveys (Bayliss and Hutton 2017). The number of dugongs in the Kimberley region was estimated to be 12,600 ± 601, an average density of 0.25 ± 0.02 km-2 over 67,163 km2 of coastal waters. The highest densities of dugongs in the Kimberley were found in areas with extensive seagrass habitat associated with sheltered, shallow (< 20 m deep), relatively clear water. The study by Bayliss and Hutton (2017) confirmed the importance of the coastal habitat within this IMMA, particularly in Roebuck Bay, Dampier Peninsula and Napier/Broome Bay. [/av_textblock] [/av_one_full] [av_one_full first min_height='' vertical_alignment='av-align-top' space='' margin='0px' margin_sync='true' padding='20px' padding_sync='true' border='' border_color='' radius='10px' radius_sync='true' background_color='#3c86be' src='' attachment='' attachment_size='' background_position='top left' background_repeat='no-repeat' animation='' mobile_display='' custom_class='' av_uid='av-xres7c'] [av_heading heading='Description of Qualifying Criteria' tag='h2' style='blockquote modern-quote modern-centered' subheading_active='' show_icon='' icon='ue800' font='entypo-fontello' size='' av-medium-font-size-title='' av-small-font-size-title='' av-mini-font-size-title='' subheading_size='15' av-medium-font-size='' av-small-font-size='' av-mini-font-size='' icon_size='' av-medium-font-size-1='' av-small-font-size-1='' av-mini-font-size-1='' color='custom-color-heading' custom_font='#ffffff' subheading_color='' seperator_color='' icon_color='' margin='' margin_sync='true' padding='10' icon_padding='10' headline_padding='' headline_padding_sync='true' link='' link_target='' id='' custom_class='' template_class='' av_uid='av-wfmymg' sc_version='1.0' admin_preview_bg=''][/av_heading] [/av_one_full] [av_one_full first min_height='' vertical_alignment='av-align-top' space='' margin='0px' margin_sync='true' padding='0px' padding_sync='true' border='' border_color='' radius='0px' radius_sync='true' background_color='' src='' attachment='' attachment_size='' background_position='top left' background_repeat='no-repeat' animation='' mobile_display='' custom_class='download' av_uid='av-uvrn7s'] [av_textblock textblock_styling_align='' textblock_styling='' textblock_styling_gap='' textblock_styling_mobile='' size='' av-medium-font-size='' av-small-font-size='' av-mini-font-size='' font_color='' color='' id='' custom_class='' template_class='' av_uid='av-tf8cso' sc_version='1.0' admin_preview_bg=''] Criterion A – Species or Population Vulnerability
Three of the four primary species relevant to this IMMA, dugong, Australian humpback dolphin and Australian snubfin dolphin, are all listed as Vulnerable by IUCN. This criterion may be particularly relevant for dugong as there is an estimated population of over 12,000 dugongs inhabiting the Kimberley region (Bayliss and Hutton, 2017) which represents more than 1% of the global population.
Criterion B: Distribution and Abundance
Sub-criterion B1: Small and Resident Populations
Known resident populations of dolphins occur in Roebuck Bay (Brown et al., 2014a, 2016ab, Raudino et al., 2019a), Cygnet Bay, Cone Bay (Brown et al., 2016ab) and Prince Regent River (Raudino et al., 2019b). The three coastal dolphin species occur in low densities with limited connectivity between communities more than 100 km apart (Brown et al., 2016a). Relatively small populations of these species were identified at specific sites across the Kimberley, typically consisting of fewer than 60 individuals. Roebuck Bay was identified as particularly important for snubfin dolphins, with the highest density of this species anywhere in its range. Humpback dolphins were present in low numbers at all sites which may reflect their larger home ranges. Calves of Australian snubfin, Australian humpback and Indo-pacific bottlenose dolphins, and dugongs have been recorded across the IMMA. Given the residency of the three dolphin species at some sites and recorded presence of calves, these sites must be significant for these species at least. This would include Roebuck Bay (Brown et al., 2014b, Raudino et al., 2019a), Cygnet Bay (Brown et al., 2014a, 2016), Prince Regent River (Raudino et al., 2019b).
Criterion C: Key Life Cycle Activities
Sub-criterion C2: Feeding Areas
The area contains some large tidal rivers, productive rocky reefs and stands of mangroves that provide fish prey for relatively large resident populations of Australian snubfin, Australian humpback and Indo-Pacific bottlenose dolphins. Foraging behaviour of these three species has been observed across the region although the types of habitat that provide foraging resources vary. Foraging habitat within the IMMA includes rocky reefs, seagrass beds and mangroves, which all have associated fish assemblages that provide suitable prey for dolphins. Foraging behaviour has been observed and described for snubfin dolphins in Roebuck Bay (Brown et al., 2014b, Raudino et al., 2019a) and Prince Regent River (Raudino et al., 2019b). Seagrass beds are present and provide a foraging resource for dugongs. Predictive seagrass habitat mapping as well as seagrass surveys have aligned well with distribution maps of dugongs (Bayliss and Hutton 2018, Campbell et al., 2010).
Criterion D: Special Attributes
Sub-criterion D1: Distinctiveness
Snubfin dolphins have been observed engaged in a specialised foraging strategy that, so far, has only been seen in this species in Western Australia, despite extensive studies on this species in other parts of Australia (e.g. Northern Territory: Palmer et al., 2014; Queensland: Para et al., 2006). The technique of spitting has been observed whereby an individual spits a stream of water at the surface, presumably to startle fish in front of the animal and scare them back towards the dolphin (the closely related Irrawaddy dolphin, Orcaella brevirostris, is the only other cetacean known to do this). Spitting behaviour has been documented in Roebuck Bay, Prince Regent River and Cygnet Bay (Raudino et al., 2019a, b). Several hybrids between a female Australian snubfin and a male Australian humpback dolphin have been observed in the Kimberley (Brown et al., 2014a).
Anonymous, 2012. ‘National Conservation Strategy and Action plans for Dugongs and their habitats in India.’ Ministry of Environment, Forests and Climate Change, New Delhi.
Apte, D., D. Parasharya & B. Patel. 2019. Feeding trails of Dugong Dugong dugon (Müller, 1776) (Mammalia: Sirenia: Dugongidae) in the Gulf of Kachchh, western coast of India. Journal of Threatened Taxa 11(1): 13151–13154; https://doi.org/10.11609/jott.43188.8.131.5251-13154
Pathan, S. 2019. Field Report Submitted to the CAMPA Dugong Recovery Project, Wildlife institute of India, Dehradun, India.
Sivakumar, K. and Nair, A. 2013. Dugong Distribution, Habitat and Risks Due to Fisheries and Other Anthropogenic Activities in India. Wildlife Institute of India – Technical Report. 1-74
Sutaria, D., Panicker, D., Jog, K., Sule, M., Muralidharan, R., and Bopardikar, I. 2015. Humpback Dolphins (Genus Sousa) in India: An Overview of Status and Conservation Issues. In ‘Conservation status of Humpback Dolphins (Sousa spp.). T.A.Jefferson and B.E.Curry (Ed.) Advances in Marine Biology Series. Vol. 72. Elsevier/Academic Press.
Sutaria, D., Arthur, R., & Satashivam, K. 2014. Marine mammals in subcontinental waters. In Mammals of South Asia: Johnsingh, A. J. T. & Manjrekar, N. (Ed.). New Delhi: Permanent Black.
Sutaria, D., and Jefferson, T. A. 2004. Records of Indo-Pacific Humpback Dolphin (Sousa chinensis Osbeck, 1765) along the coast of India and Sri Lanka – An Overview. Aquatic Mammals Special Issue 30(1) 125-136
MMRCNI 2019. Database on Sousa plumbea and Neophocaena phocaenoides from Gujarat: www.marinemammals.in
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