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Waterbirds on an Adjacent Freshwater Lake and Salt Lake in Arid Australia

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Waterbirds on an Adjacent Freshwater Lake and Salt Lake in Arid Australia Biological Conservation 69 (1994) 219-228 © 1994 Elsevier Science Limited Printed in Great Britain. All rights reserved 0006-3207/94/$07.00 ELSEVIER WATERBIRDS ON AN ADJACENT FRESHWATER LAKE AND SALT LAKE IN ARID AUSTRALIA R. T. Kingsford & J. L. Porter National Parks and Wildlife Service (NSW), PO Box 1967, Hurstville, NSW 2220, Australia (Received 21 May 1993; revised version received 20 July 1993; accepted 20 July 1993) Abstract salt lakes (Chessman & Williams, 1974; Hart et al., Aerial surveys of waterbirds were made on Lake Wyara 1991), and numbers of macrophyte and invertebrate (salt) and Lake Numalla (freshwater) in arid Australia, species are low (De Deckker, 1983; Brock, 1985; Bolen every three months, 1987-1989. These lakes were signifi- et al., 1989; Hart et al., 1991; Seaman et al. 1991). cant sites for conservation of waterbirds. Aerial counts Numbers of waterbird species may also decline with in- were on average 42 000 waterbirds (2600-113 500), in- creasing salinity (Timms, 1981), but there are few stud- cluding at least 41 species. In March 1988, total numbers ies comparing the abundance of organisms in probably exceeded 280 000. More than half the popula- freshwater and salt lakes. tion of freckled duck Stictonetta naevosa may occur on We investigated abundance and diversity of water- the lakes. Although only 3 km apart and similar in size, birds on two wetlands in arid Australia, Lakes Wyara the salt lake had about ten times more waterbirds and Numalla, over a three-year period. These wetlands /mainly ducks, herbivores, small wading birds) than the were similar in size and were only about 3 km apart freshwater lake (mainly piscivores, large wading birds). but one is a salt lake and the other freshwater. We Differences in waterbird communities between the lakes know of nowhere else in Australia where the effect of were attributable to food resources. There were larger salinity on a waterbird community can be examined numbers of planktonic invertebrates and more macro- without undue influence from the confounding factors phyte vegetation in the salt lake than in the freshwater of size and distance between wetlands. Our objectives lake while the freshwater lake contained fish and shrimp were to determine the significance of these wetlands to populations. waterbirds, and to compare the abundance and diver- sity of their waterbirds and propose a hypothesis to ac- Keywords: Australia, waterbirds, arid, freshwater, salt. count for patterns observed. Nomenclature for birds follows Marchant and Higgins (1990), and for vascular plants follows Harden INTRODUCTION (1990). Wetlands in arid regions of the world can be fresh water but, because of high evaporation, are more often METHODS saline (Bayly & Williams, 1973; De Deckker, 1983; Sea- man et al., 1991). Freshwater and salt wetlands, many Study area of which flood temporarily, are ubiquitous in arid Aus- Lake Numalla (2904 ha, 28°44'S, 144°18'E) is a fresh- tralia (Williams, 1981) which makes up about 70% of water lake and Lake Wyara (3813 ha, 28°42'S, the continent (Stafford Smith & Morton, 1990). These 144°14'E) a salt lake in south western Queensland (Fig. wetlands had not been considered important for water- 1). Annual rainfall measured at Boorara Station, 10 km fowl (Frith, 1982) because more valuable waterbird north-east of Lake Numalla, was 431 mm, 398 mm, habitats are thought to be in the tropics (Lavery, 1970; and 255 mm respectively during the three years of the Morton et al., 1990, 1993a, b) and the south of the con- study, 1987-1989. tinent (Frith, 1982; Halse et al., 1990). Nevertheless Six creeks run into Lake Wyara from unnamed there is increasing evidence that some wetlands in arid ranges in the west and the south and from Willies and Australia support particularly large numbers of water- Waiters Ranges in the north (Fig. 1). Ruppia sp., Chara birds (Braithwaite et al., 1986; Halse, 1990; Kingsford australis and Lamprothamnium papulosum, submerged et al., 1990; Reid & Puckeridge, 1990; Maher & Braith- macrophytes, grew extensively across the bottom of waite, 1992; Kingsford & Porter, 1993). Lake Wyara, and salt-tolerant plant species, such as Despite the world-wide abundance of salt lakes (sim- samphire Halosarcia pergranulata and creeping monkey ilar in volume to fresh waters), they are generally re- flower Mimulus repens, around the edge. When full, garded as less important than freshwater wetlands Lake Wyara has three islands along its western shore- (Williams, 1988). Comparative diversity of biota has re- line (Fig. 1). inforced this view. Fish and frogs are seldom found in Lake Numalla receives water from Boorara Creek 219 220 R. T. Kingsford, J. L. Porter marked divisions on the window of the aircraft on two .~wilka C~ke W BooraraCk trips. Some waterbird breeding data were collected on 17 August 1989. We estimated the number of nests of a colony of Australian pelicans occupying the centre of the island (210 m x 10 m) and counted the nests of black swans and their clutch sizes. To estimate pelican nests which were uniformly spaced within the nesting area, we extrapolated a count for a 10-m length of the strip. Colonies of silver gulls and Caspian terns were independently estimated by three observers. Invertebrate sampling We sampled invertebrates from the two lakes 14-16 August 1989. Twenty samples of zooplankton were col- lected randomly from areas of high and low waterbird abundance on each lake (determined during aerial sur- veys). We used a 2-m perspex tube, 54 mm in diameter, N CarwarraCk which was lowered vertically through the water column until either the top end was just above the surface of the water or the bottom end came into contact with the substratum. The column of water was secured with 0 km 5 corks and the volume measured before the water was Fig. 1. Location of Lakes Numalla (freshwater) and Wyara flushed through a 75-/~m sieve, designed to catch (salt). N marks islands where there was evidence of nesting macroinvertebrates (Bottrell et al., 1976). Invertebrates on Lake Wyara. were fixed in a solution of 4% formalin with 60 g litre J of sugar (Prepas, 1978) and identified, mostly to Order, draining the eastern slope of Walters and Hoods and counted under a binocular microscope using a Ranges, and Carwarra Creek which runs from the rafter chamber (Newell & Newell, 1973). All samples Paroo River (Fig. 1). It is surrounded by dead and liv- for each lake were combined; species composition and ing black box Eucalyptus largiflorens, coolibah E. mi- body lengths and widths of the invertebrate species crotheca and river cooba Acacia stenophylla. Patches of recorded were determined in 10 subsamples (1 ml). spiny sedge Cyperus gymnocaulos fringe the lake. In the Ten wooden boards (90 mm x 200 mm) on floats southern and northern ends, clumps of lignum were placed randomly across each lake, 5-10 cm above Muehlenbeckia florulenta occur. the water during the same 24-h period. They were cov- ered by plastic bags coated with the sticky preparation Waterbird counts Tanglefoot (Tanglefoot Company, Grand Rapids, Beginning in March 1987, surveys were flown over the USA). Plastic bags avoided Tanglefoot contact with the lakes every three months until December 1989 in a boards and could be easily slipped off. Sampling was Cessna 206 aircraft at a height of 30 m and a speed of repeated 24-h later after a millimetre of rain fell on the 167 km h -~. Two observers, one on each side of the air- first night. After collection, invertebrates on these craft, identified and estimated total numbers of water- 'sticky-traps' were identified to Family, where possible, birds and recorded this information on mini cassette and counted. recorders. Most waterbirds could be identified to Five one-litre samples of water were collected ran- species, but four groups of species could not (Appendix domly from each lake and frozen. Ionic composition, 1, see also for scientific names). Where possible, brood total dissolved solids, total phosphorus and CaCO3 in sizes were also recorded. Each lake was counted four the water were determined (Franson, 1981). Conductiv- times during each three-month trip because aerial sur- ity and pH (PTI-52 meter, CHK Engineering, Sydney), veys of many species of waterbirds were prone to large and Secchi disk readings were collected with samples of random error (R.T. Kingsford, unpublished data). Two the water column. Average depth was calculated from surveys were flown without delay and repeated within ten random locations along an east-west transect. two days. The four counts were used to calculate means and standard errors for each three-month trip. Statistical analysis The aircraft was flown over water about 150 m from Water chemistry variables were compared between the edge of the lake, where waterbirds concentrated. To lakes using Student t- or Kruskal-Wallis tests where as- determine numbers of birds missed, distribution and sumptions of the former were not met (Sokal & Rohlf, abundance of waterbirds were recorded on five tran- 1981). We used Wilcoxon signed ranks tests to compare sects, 100 m wide, flown randomly across Lake Wyara numbers of waterbirds, and nests and broods of black on each of five trips. Distances of all waterbirds from swans between the two lakes. Each data point was the the shore on Lake Numalla were estimated using mean of four aerial estimates. Waterbirds were sepa- Waterbirds on freshwater and salt lakes 221 rated into four foraging groups: piscivores and large 100000 wading birds; ducks and little grebes; herbivores and 80000 small wading birds (see Appendix 1). Groups were ,-a based on the food that they eat (Barker & Vestjens, 60000 1989; Marchant & Higgins, 1990) and where the birds Z .~ 40000 usually forage (Kingsford, 1991).
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