| Taxon Attribute Profiles 
         
          |  Macquarie Turtle Emydura macquarii
 (photo: John Wombey)
 |  Chelidae freshwater turtles   Taxonomy and Ecology Synopsis of included taxaThe family Chelidae is endemic to Australia, New Guinea, and South America 
        and consists of some 40 species of freshwater turtle. Twenty-four described 
        species are found in Australia and three of these occur in the Murray 
        Darling Basin: Chelodina expansa (Broad-shelled Turtle), Chelodina 
        longicollis (Snake-necked Turtle), and Emydura macquarii (Macquarie 
        Turtle). These are "side-necked" turtles, so named because the 
        neck and head, when not extended, fold under the leading edge of the carapace, 
        and they are further characterised by their relatively flattened shells 
        and their clawed webbed feet (Wilson and Swan 2003). Life Form/Morphology
         
          |  Snake-necked Turtle Chelodina longicollis
 (photo: John Wombey)
 |  Turtles of the genus Chelodina are distinguished by their exceptionally 
        long necks. C. expansa is the largest of Australias freshwater 
        turtles: its carapace (upper shell) measures up to 48 cm in length and 
        its long thick neck, when outstretched, adds another 80% to its overall 
        body length. C. longicollis is a medium-sized turtle, its carapace 
        measuring up to 25 cm in length, with a long slender neck. Apart from 
        size, adults of the two species are differentiated by the white iris, 
        neck tubercles, and broad black sutures on the plastron (lower shell) 
        of C. longicollis. The light olive to dark brown carapace of C. 
        expansa also averages lighter in colour than that of C. longicollis, 
        which is dark brown to black, and the plastron of the juvenile C. longicollis 
        is distinctively marked with black and red-orange (Cann 1998).  Emydura species have much shorter necks than those of Chelodina. 
        E. macquarii is a brown turtle with a pale yellow or cream stripe 
        extending from the mouth back along the neck. The nominate race, which 
        inhabits the Murray Darling Basin, is large (carapace length to 34 cm) 
        and has a distinctive yellow iris.
  Distribution
 C. expansa, C. longicollis, and E. macquarii are 
        restricted to eastern Australia and are widespread in the Murray Darling 
        Basin. The ranges of C. expansa and C. longicollis extend 
        additionally to the southeast Queensland coast, C. expansa north 
        to Rockhampton and offshore to Fraser Island and C. longicollis 
        north to the Townsville region. C. longicollis is also widespread 
        in coastal drainages of New South Wales and Victoria. The subspecies E. 
        m. macquarii is endemic to the Murray Darling Basin; other races of 
        this species are found in coastal New South Wales and southeast Queensland. HabitatC. expansa is typically found in turbid water at the bottom of 
        rivers and permanent streams and waterholes, lying concealed among debris 
        or among root-mats. C. longicollis prefers swamps, oxbow lakes, 
        billabongs, and slow-moving weedy rivers and streams, but can also occur 
        in swift-flowing watercourses and can be found dispersing overland. E. 
        macquarii occurs along rivers, creeks and lagoons, often in larger 
        rivers and large waterholes; it is frequently seen basking on emergent 
        logs or rocks. Role in CommunityRoles in the community differ substantially among the three species: 
        C. expansa is a specialised predator, C. longicollis an 
        opportunistic carnivore, and E. macquarii an opportunistic omnivore. 
        C. expansa uses ambush tactics on highly mobile prey, its neck 
        striking out like a snake. Most commonly eaten prey items are decapod 
        crustaceans (notably crayfish and prawns), aquatic insects (Hemiptera), 
        and small fish (Chessman 1983). C. longicollis feeds primarily 
        on planktonic crustaceans (mostly Cladocera), fish carrion, prawns, corixids 
        (Hemiptera), chironomids (Diptera), and small fish, and its diet varies 
        depending on the type of water body occupied (Chessman 1984). E. macquarii 
        has an extremely varied diet, consisting largely of filamentous algae, 
        vertebrate carrion, detritus, periphyton, aquatic insects, and aquatic 
        plants (Chessman 1986). However, carrion and invertebrates appear to be 
        essential dietary items for this species, owing to its inability to meet 
        its metabolic requirements solely from macrophytes (Spencer et al. 1998).  Reproduction and Establishment ReproductionLittle is known about courtship and mating of turtles in the Murray Darling 
        Basin, although mating of C. longicollis has been observed in April-May 
        and September-October and in captivity in January. Mating of E. macquarii 
        in captivity has been observed in January and in March-April (Cann 1998). 
        When ready to nest, females leave the water to excavate a nest hole, lay 
        their eggs, bury the nest, and return to the water, leaving the eggs to 
        incubate on their own. Nest-site selection in at least one species (E. 
        macquarii)  and probably others  is a trade-off between 
        minimising predation on the laying female, which increases further from 
        shore, and nest predation, which increases closer to shore (Spencer and 
        Thompson 2003). C. expansa nests mainly March-May, C. longicollis 
        September-December, and E. macquarii November-December, although 
        nesting can occur at other times of the year, especially following substantial 
        rains (Cann 1998). Nests of these species are generally close to water, 
        but can be up to 1 km distant. From 5-30 eggs are laid (typically 10-15) 
        and natural incubation periods range from 65-85 days in E. macquarii 
        and 120-180 days in C. longicollis to some 200-650 days in C. 
        expansa (Goode and Russell 1968; Cann 1998). Sex determination in 
        at least two of these species (C. longicollis and E. macquarii) 
        is not dependent on temperature (Georges 1988). DispersabilityTerrestrial movements are important features in the life histories of 
        freshwater turtles; movements may be necessitated by such factors as habitat 
        loss, food shortage, and rainfall events (Graham et al. 1996). Movements 
        of C. longicollis are well documented: this species is often found 
        a considerable distance from water and has been shown to possess navigational 
        abilities. Non-nesting movements of C. expansa and E. macquarii 
        are not as well known, although they likely occur occasionally in response 
        to climatic factors. Juvenile PeriodMale E. macquarii and C. expansa mature at 5-6 years and 
        9-11 years, respectively, and females at 9-11 years and 14-15 years, respectively. 
        Young E. macquarii exhibit rapid juvenile growth followed by a 
        decline in growth rate towards maturity, whereas young C. expansa 
        grow more slowly during their first 3-4 years (Spencer 2002).  Hydrology and Salinity Flooding RegimesAlternating periods of flooding and drought could affect freshwater turtles, 
        owing to the limited dispersal ability of some species.  Conservation Status Although C. longicollis is considered of least concern, C. 
        expansa and E. macquarii are presumed threatened but are too 
        rare or insufficiently known for conservation status to be assessed accurately 
        (Cogger 1993). Freshwater turtles are vulnerable to many human and natural 
        factors. For example, large numbers of these turtles are accidentally 
        caught and drowned in drum-nets and they are quite vulnerable to changes 
        in water levels brought on by drought and human water-use. Chelids occasionally 
        succumb to unknown pressures: several hundred E. macquarii, for 
        instance, were unaccountably found dead at Lake Boga, South Australia, 
        during the first half of 1976, while many others were clearly emaciated 
        (Cann 1998). Predators are also a threat to freshwater turtles of the 
        Murray Darling Basin, especially to nests and hatchlings. A study of nesting 
        along the Murray found that 96% of nests of C. expansa, C. longicollis, 
        and E. macquarii had been depredated, mainly by foxes but also 
        by water-rats, goannas, and ravens (Thompson 1983).  Uses Freshwater turtles are collected and eaten by aboriginal people and Europeans 
        in many regions of Australia, and large numbers are known to be taken 
        in parts of New South Wales (Cann 1998).  Summary Chelid turtles of the Murray Darling Basin form a suite of three co-existing 
        species of differing diet and habitat preferences. Changes in abundance 
        of these species may serve as useful indicators of the abundance of their 
        respective prey items and of waterway health generally.  References Cann, J. 1998. Australian freshwater turtles. Beaumont Publ., 
        Singapore. Chessman, B. C. 1983. Observations on the diet of the broad-shelled turtle, 
        Chelodina expansa Gray (Testudines: Chelidae). Australian Wildlife 
        Research 10:169-172. Chessman, B. C. 1984. Food of the snake-necked turtle, Chelodina longicollis 
        (Shaw) (Testudines: Chelidae) in the Murray Valley, Victoria and New South 
        Wales. Australian Wildlife Research 11:573-578. Chessman, B. C. 1986. Diet of the Murray turtle, Emydura macquarii 
        (Gray) (Testudines: Chelidae). Australian Wildlife Research 13:65-69. Cogger, H. G., Cameron, E. E., Sadlier, R. A., and P. Eggler. 1993. The 
        action plan for Australian reptiles.  Australian Nature Conservation 
        Agency, Canberra. Georges, A. 1988. Sex determination is independent of incubation temperature 
        in another chelid turtle, Chelodina longicollis. Copeia 
        1988:249-255. Goode, J, and J. Russell. 1968. Incubation of eggs of three species of 
        chelid tortoises, and notes on their embryological development. Australian 
        Journal of Zoology 16:749-761. Graham, T., Georges, A., and N. McElhinney. 1996. Terrestrial orientation 
        by the Eastern Long-necked Turtle, Chelodina longicollis, from 
        Australia. Journal of Herpetology 30:467-477. Spencer, R. 2002. Growth patterns of two widely distributed freshwater 
        turtles and a comparison of common methods used to estimate age. Australian 
        Journal of Zoology 50:477-490. Spencer, R., Thompson, M. B., and I. D. Hume. 1998. The diet and digestive 
        energetics of an Australian short-necked turtle, Emydura macquarii. 
        Comparative Biochemistry and Physiology Part A 121:341-349. Spencer, R., and M. B. Thompson. 2003. The significance of predation 
        in nest site selection of turtles: an experimental consideration of macro- 
        and microhabitat preferences. Oikos 102:592-600. Thompson, M. B. 1983. Population of the Murray River tortoise Emydura 
        (Chelidae): the effect of egg predation by the red fox, Vulpes vulpes. 
        Australian Wildlife Research 10:363-371. Wilson, S. and G. Swan. 2003. A complete guide to the reptiles of 
        Australia. New Holland Publ., Sydney. |