ISRA FACTSHEETS
ISRA FACTSHEETS
AUSTRALIA AND SOUTHEAST INDIAN OCEAN
Ashmore-Coral Sea
Summary
Ashmore-Coral Sea is located in the northwest Coral Sea, off Queensland, Australia. It encompasses the southern part of a reef lagoon and sections of outer reef. The area is situated on top of an extinct underwater volcano and is characterised by an extensive and deep reef lagoon, coral reefs, and steep outer walls. It is influenced by its shelf-edge geomorphology, strong tidal currents, seasonal wind regimes, and the Hiri Current. The area overlaps with the Coral Sea Marine Park. Within this area there are: threatened species and undefined aggregations (Grey Reef Shark Carcharhinus amblyrhynchos).
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Ashmore-Coral Sea
DESCRIPTION OF HABITAT
Ashmore-Coral Sea is located in the northwest Coral Sea, off Queensland, Australia. It encompasses the southern part of the reef lagoon and part of the eastern and western outer reefs. The area is situated on top of an extinct underwater volcano, ~46 km east of the outer reefs of Torres Strait. It is characterised by an extensive and deep reef lagoon, coral reefs, and steep outer walls, dropping to >500 m depth within a few hundred metres (Galbraith et al. 2022; Hoey et al. 2024).
The area is influenced by its shelf-edge geomorphology, strong tidal currents, seasonal wind regimes, and the Hiri Current, which branches north from the South Equatorial Current to form a slow clockwise gyre in the Gulf of Papua. North-westerly monsoon winds in the austral summer and south-easterly trade winds in winter drive low-frequency circulation (Church et al. 1988). The area benefits from seasonal upwelling when the poleward boundary current along the shelf is weakened or reversed by eddies forming in the Gulf of Papua (Condie & Dunn 2006).
Ashmore-Coral Sea overlaps with the Coral Sea Marine Park – National Park Zone (Parks Australia 2025).
This Important Shark and Ray Area is benthic and pelagic and is delineated from 0–40 m based on the bathymetry of the area.
CRITERION A
VULNERABILITY
One Qualifying Species considered threatened with extinction according to the IUCN Red List of Threatened Species regularly occurs in the area. This is the Endangered Grey Reef Shark (Simpfendorfer et al. 2020).
CRITERION C
SUB-CRITERION C5 – UNDEFINED AGGREGATIONS
Ashmore-Coral Sea is an important aggregation area for one shark species.
Grey Reef Sharks have been observed aggregating in the area. In 2018, 2021, and 2023, diver-based underwater visual census (UVC) surveys were conducted in the area and other reefs outside of this area in the Coral Sea (Galbraith et al. 2022; Hoey et al. 2024). Diver-based surveys were conducted at 12 shallow reef sites across Ashmore (>130 diver hours). At each site, three replicate 50 m transects were run parallel to the depth contour, with up to 10 m between successive transects (Hoey et al. 2024). Grey Reef Sharks were regularly observed at Ashmore-Coral Sea, with a total estimation of 20 sharks per hectare. Sharks were generally more abundant on the exposed eastern side of the reefs, compared to the lagoon or sheltered western reefs (outside the area). Grey Reef Sharks were juveniles and adults, measuring between 110–180 cm total length (TL) obtained through visual estimation (A Hoey & E McClure unpubl. data 2025). Size-at-birth for the species is 45–64 cm TL and size-at-maturity is 160–200 cm TL (Ebert et al. 2021).
Additionally, between 2023–2025, 2–4 dive trips per year (12–20 dives per trip) were conducted in the area during April and November (P Cogollos unpubl. data 2025). Aggregations of 3–6 Grey Reef Sharks were observed on 100% of the dives (~24–80 dives per year) within the area by dive guides collecting opportunistic data during SCUBA dives (P Cogollos unpubl. data 2025). These Grey Reef Sharks were between neonatal and adult life-stages, measuring between 50–200 cm TL (P Cogollos unpubl. data 2025).
Grey Reef Sharks have shown high residency and site fidelity to similar reefs in the Coral Sea and the Great Barrier Reef, highlighting the individual importance of reefs such as this area (Espinoza et al. 2015). Due to the remoteness of the area, observations are opportunistic, but the large numbers of individuals and predictability of aggregations reported across different years highlight the importance of this area. Further information is required to understand the nature and function of these aggregations.
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