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ISRA FACTSHEETS

AUSTRALIA AND SOUTHEAST INDIAN OCEAN

ISRA FACTSHEETS

AUSTRALIA AND SOUTHEAST INDIAN OCEAN

Burrill Lake ISRA

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Burrill Lake ISRA

Burrill Lake

Summary

Burrill Lake is located on the south coast of New South Wales, Australia. It is a small estuary connected to the sea by a narrow channel. It is characterised by seagrass beds and sandy and muddy substrates. Within this area there are: threatened species (Estuary Stingray Hemitrygon fluviorum); and feeding areas (e.g., Common Stingaree Trygonoptera testacea).

Burrill Lake

DESCRIPTION OF HABITAT

Burrill Lake is located on the south coast of New South Wales, Australia. It is a small estuary connected to the Pacific Ocean by a narrow channel (~3 km in length) in the south. A sand barrier fills the channel producing a periodical separation from the sea and a flood-tide delta in the central part of the estuary (Sloss et al. 2006). The area is characterised by seagrass beds and sandy and muddy substrates (Jones et al. 2003). It receives freshwater input from Stony Creek and is dominated by wave dynamics.

The area is permanently open to the sea with a tidal range of <0.3 m (Hutchings et al. 1978). Sea surface temperature ranges from ~13°C in August to ~27°C in January (Ajani et al. 2022).

This Important Shark and Ray Area is benthic and is delineated from inshore and surface waters (0 m) to 2 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 Vulnerable Estuary Stingray (Hyde et al. 2025).

CRITERION C

SUB-CRITERION C2 – FEEDING AREAS

Burrill Lake is an important feeding area for two ray species.

Estuary Stingrays and Common Stingarees feed regularly and predictably in Burrill Lake (Grew 2025). Targeted drone surveys (transects and tracking of individual rays) were conducted between January 2022–May 2024 (Grew 2025). Transects (450 m straight) were conducted across the estuary at 30 m altitude and covered seagrass and bare substrates. A maximum of 16 transects were conducted per day. Locations identified during transect surveys were searched for Estuary Stingrays and Common Stingarees and when an individual was sighted the drone was moved to 5 m altitude and the individual was followed until it was lost or the battery ran out. Multiple observations were recorded for a single individual tracked. Between 30–50 individual tracks were conducted per season (Grew 2025).

In the transect surveys, 99 rays from both species were recorded (Grew 2025). Both species were mostly observed swimming (64 instances, 64.6%) with foraging being the second most commonly observed behaviour (19 instances, 19.2%). Individuals from both species were observed mostly around bare substrates (75 instances, 75.8%) compared to seagrass (24 instances, 24.2%). In addition, 120 Estuary Stingrays and 144 Common Stingarees were individually tracked. The most common behaviours for Estuary Stingrays were swimming (n = 94 observations, 32.6%) and foraging (n = 74, 25.7%) in bare substrates. For Common Stingarees, swimming was the most observed behaviour (n = 134 observations, 36.8%), followed by foraging (n = 90, 24.7%; Grew 2025). While the diet of both species was not assessed, in other regions (e.g., Wallis Lake), Estuary Stingrays use similar bare substrate habitats for feeding on highly abundant benthic fish and crustaceans that aggregate to spawn. Bare substrates may be a preferred habitat for both species due to the higher accessibility to prey compared to other substrates (Grew et al. 2025).

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