2.4.9 Sea snakes

Sea snakes, although the most diverse group of marine reptiles, have received relatively little scientific attention.427 There are two groups of sea snakes: the amphibious sea kraits and the marine ‘true’ sea snakes.427 True sea snakes produce live young and are entirely marine, never venturing onto land. Offshore marine species retain traits from their terrestrial ancestors, such as needing to drink fresh water obtained from lenses that form on the surface of the ocean after rainfall.428,429 Sea snakes are important ecologically as predators and have been used as bio-indicators for cryptic species of fish.427

The Region forms part of a global hotspot of sea snake diversity that encompasses northern Australia and the Indonesian–Malaysian archipelago. Sixteen species of true sea snakes have been recorded in the Region, and 14 maintain permanent breeding populations.430 Most are benthic foraging species, but different species are associated with different habitats.431 The highest density and diversity of sea snakes are found in the central and southern Reef, and species like the olive sea snake and spine-bellied sea snake are commonly recorded in inshore bays and fringing reefs along the Queensland coast.427

Low reproductive output and limited dispersal capability limit recovery potential 

Sea snakes have a low reproductive output and limited dispersal capability limiting their potential for population recovery and recolonisation when populations are affected.432,433 Studies on sea snake movements on the Reef have shown that some species are highly attached to specific reefs, for example, olive sea snakes 427 and turtle-headed sea snakes 434 do not venture far from their home reef. During the mating season, males increase their movements to find females on the same reef, and seasonal aggregations of sea snakes are often observed in areas with large populations.427 The limited capability of sea snakes to disperse between reefs can result in highly fragmented populations 435 such as found in the Swain Reefs and Pompey Reef complex in the southern region.427

Long-term population trend data are severely limited. Densities of sea snakes at Marion Reef, east of Airlie Beach, declined by more than 80 per cent between 2012 and 2017,436 whereas populations in other areas (for example, Cleveland Bay) are considered stable.427 The extent and underlying causes of population declines remain uncertain. Most species of sea snakes are considered to be at medium risk from interactions with trawl fisheries in Queensland, and bycatch mitigation strategies to quantify and reduce mortalities are being advanced in collaboration with industry.437 

Despite reported declines in some locations, the lack of systematic population monitoring means the status of sea snakes in the Region remains uncertain. Based on the limited available evidence, the condition of sea snakes in the Region is inferred to be stable.

An olive sea snake swims over coral rubble with a swarm of small fish behind it.
Sea snake at Yongala shipwreck © Pablo Cogollos 2023
References
  • 427. Udyawer, V. and Heatwole, H. 2022, Sea snakes: a unique group of marine reptiles, in Coral Reefs of Australia: Perspectives from Beyond the Water's Edge, eds S.M. Hamylton, P. Hutchings and O. Hoegh-Guldberg, CSIRO Publishing, Australia, pp. 166–167.
  • 428. Lillywhite, H.B., Sheehy III, C.M., Sandfoss, M.R., Crowe-Riddell, J. and Grech, A. 2019, Drinking by sea snakes from oceanic freshwater lenses at first rainfall ending seasonal drought, PLoS One 14(2): e0212099.
  • 429. Lillywhite, H.B., Babonis, L.S., Sheehy III, C.M. and Tu III, M. 2008, Sea snakes (Laticauda spp.) require fresh drinking water: implication for the distribution and persistence of populations, Physiological and Biochemical Zoology 81(6): 785-796.
  • 430. Heatwole, H. and Lukoschek, V. 2008, Reptiles, in The Great Barrier Reef: Biological, Environment and Management, eds P. Hutchings, M. Kingsford and O. Hoegh-Guldberg, CSIRO Publishing, Collingwood, pp. 343-349.
  • 431. Hamann, M., Limpus, C.J. and Read, M.A. 2008, Vulnerability of marine reptiles in the Great Barrier Reef to climate change, in Climate Change and the Great Barrier Reef: A vulnerability assessment, eds P.E. Johnson and P.A. Marshall, Great Barrier Reef Marine Park Authority and Australian Greenhouse Office, Townsville, pp. 466-496.
  • 432. Somaweera, R., Udyawer, V., Guinea, M.L., Ceccarelli, D.M., Clarke, R.H., et al. 2021, Pinpointing drivers of extirpation in sea snakes: a synthesis of evidence from Ashmore Reef, Frontiers in Marine Science 8: 658756.
  • 433. Fry, G.C., Milton, D.A. and Wassenberg, T.J. 2001, The reproductive biology and diet of sea snake bycatch of prawn trawling in northern Australia: characteristics important for assessing the impacts on populations, Pacific Conservation Biology 7(1): 55-73.
  • 434. Lukoschek, V. and Shine, R. 2012, Sea snakes rarely venture far from home, Ecology and Evolution 2(6): 1113-1121.
  • 435. Shine, R., Brown, G.P. and Goiran, C. 2022, Divergence in life-history traits among three adjoining populations of the sea snake Emydocephalus annulatus (Hydrophiinae, Elapidae), Scientific Reports 12(1): 5137.
  • 436. Edgar, G.J., Cooper, A.T., Baker, S.C., Barker, W., Barrett, N.S., et al. 2020, Reef life survey: establishing the ecological basis for conservation of shallow marine life, Biological Conservation, 252.
  • 437. Dedini, E., Jacobsen, I. and Zieth, J. 2023, East Coast Otter Trawl Fishery ecological risk assessment species of conservation concern, State of Queensland, Brisbane.