Output list
Conference presentation
Published 2013
Invited speaker at Department of Fisheries workshop- “Marine heatwave- 2 years on”, 11/03/2013, Perth, Western Australia
Conference presentation
Published 2013
Invited speaker at South West Marine Conference, 09/05/2013, Bunker Bay, Western Australia
Journal article
Published 2012
Marine and Freshwater Research, 63, 10, 914 - 925
Using 20 years of data (1986 to 2008), we examined relationships between oceanographic variables (Fremantle sea level (FSL) a proxy for the strength of the Leeuwin Current and sea surface temperature (SST)) and five measures of little penguin, Eudyptula minor, breeding performance near Perth, Western Australia: namely (1) the laying date, (2) the number of chicks produced per pair, (3) the proportion of eggs that hatched, (4) the overall breeding success, defined as the proportion of total eggs laid that resulted in successful fledglings and (5) chick mass at fledging. The next three years of data (2009 to 2011) were used to test the performance of our statistical predictive models. FSL provided more accurate predictions of timing of laying, whereas SST provided more accurate predictions of breeding success. A later end to laying was associated with a high FSL during the summer (December to February) before breeding. Higher SSTs in the pre-breeding period from April to May corresponded to reduced breeding success, with lower fledgling success, fewer chicks per pair and generally a lower mean mass of chicks at fledging. The models predict that future oceanographic warming is expected to reduce the breeding success of this colony of little penguins.
Journal article
Published 2011
Wildlife Research, 38, 6, 491 - 500
Context Penguin Island supports the largest colony of little penguins in Western Australia. It is subjected to a suite of anthropogenic threats because of its proximity to an increasing urban population. For effective management of the colony, it is necessary to not only have knowledge of the size of the colony, but also the population trend of the colony. Aims To demonstrate a new cost-effective method of estimating the island-wide population of penguins on Penguin Island. Methods We estimated the island-wide population by combining mark-recapture sampling over 2 years on part of the island and beach counts of penguins arriving at night around the entire island. We estimated the abundance using closed population models, allowing for sex and time effects in capture probabilities. We had four capture occasions in 2008 only, and so considered heterogeneity of capture probabilities (Mh), using the Chao heterogeneity moment estimator. The proportion of all penguins counted that arrived at the four mark-recapture sites was then used to inflate the population estimate for the whole island. Key results In all, 62% of all penguins counted used the four mark-recapture sites. In 2007, there were an estimated 2369±198 penguins, and 1543±182 in 2008. When capture heterogeneity was allowed for in 2008, this estimate increased to 2069±1172. Conclusions Fewer eggs were laid and all measures of breeding performance were lower in 2008 than in 2007. Hence, the lower population estimate is most likely to represent fewer birds attempting to breed. However, further work on population estimates is required to determine whether capture heterogeneity occurs in both good and poor breeding years. Capture rates were affected by the presence of a full moon and high tides. Implications The estimate of the population can be used as part of the basis of a long-term monitoring program needed for effective management of the penguin colony. However, such studies must be coincident with the monitoring of a suite of reproductive and foraging parameters if short-term impacts of threats are to be recognised and well managed.
Conference presentation
2008: The year of the global financial crisis and the Perth penguin crisis?
Published 2010
Abstracts of the Seventh International Penguin Conference, 30/08/2010–03/09/2010, Boston, USA
Journal article
Published 2009
Journal of Zoology, 208, 2, 285 - 297
The mouse‐sized marsupial Tarsipes rostratus, endemic to south‐western Australia, feeds almost exclusively on nectar and pollen. Its tongue has long filiform papillae at the tip and shorter compound papillae over much of the upper surface. These collect nectar and pollen when the long tongue, stiffened by a keratinized keel, is protruded into flowers or over pollen presenters. Pollen is scraped from the papillae by a series of combs on the roof of the mouth. A large diverticulum, off the main chamber of the stomach, may store nectar in times of surplus. Pollen is not digested in the stomach but during passage down the simple intestine, which does not have a caecum. In captive animals, pollen passed through the gut in about six hours and the percentage of grains voided which had lost their contents was related to time spent in the gut. The digestion process remains unresolved but probably takes place through the apertures in the shells of pollen grains. Tarsipes ingests large numbers of pollen grains whose contents probably provide necessary nutrients absent from nectar.
Journal article
Published 2009
Journal of Zoology, 195, 2, 267 - 279
During 1978 and 1979 over 900 individuals of the mouse‐sized marsupial nectarivore Tarsipes spencerae were pitfall trapped in Banksia thickets on the south coast of Western Australia. In both years numbers were highest in spring, when nectar was most abundant and lowest during summer months when it was scarce. The larger number of males caught probably reflects their greater activity rather than their greater abundance.
Journal article
Published 2008
Biological Journal of the Linnean Society, 25, 4, 355 - 363
The singing honeyeater, a nectar-feeding bird, is common throughout most of Australia. There is considerable geographical variation in weight, the heaviest birds (30 g) living at the highest latitudes (35°S) and the lightest birds (19 g) at the lowest latitudes (16°S). Clinal variation in weight is apparently related to climatic factors (e.g. potential evapotranspiration) in accord with Bergmann's rule. The exceptions are populations on islands and peninsulas which are about 13% heavier than those on the adjacent mainland.
Conference presentation
Little Penguins use of Perth metropolitan waters exposes them to risk of injury from watercraft
Published 2007
Fourth Biennial Australasian Ornithological Conference, 03/12/2007–05/12/2007, Perth, Western Australia
The rapid growth of urban areas near Little Penguin colonies on Penguin and Garden islands in Perth, Western Australia, potentially increases their exposure to various threats. To identify the possible range of threats at sea, the foraging ranges and diving behaviour of the penguins have been studied. From radio tracking Penguin Island penguins and satellite tracking those from both islands, we found they generally remained within a 20 km radius of their colony during breeding. Using time depth recorders, we found the penguins travelled in the top 2m, and some penguins preferentially dived within the top 4 m. The bays used by the penguins are also used extensively for recreational and commercial activities such as fishing, boating, water skiing and windsurfing. Results of autopsies of Little Penguins showed many had injuries that were likely to be caused by watercraft.
Journal article
Published 2007
Emu, 107, 4, 275 - 283
The Flesh-footed Shearwater (Puffinus carneipes) is a pelagic seabird that breeds predominantly around southern Australia and New Zealand. Its breeding biology is poorly known, particularly in Western Australia where the species is known to have suffered mortality during long-line fishing operations. We studied the breeding biology of the Flesh-footed Shearwater on Woody Island, off the southern coast of Western Australia, between 2000 and 2003, from the post-migratory return of adults to the colony until the departure of the last fledglings 7 months later. Shearwaters dug single-tunnelled burrows slightly over 1 m long (1050 ± 16 mm (s.e.)) in soil >350 mm deep, during October, before embarking on an unsynchronised pre-laying exodus through November. Eggs were laid in the last week of November, and incubated over 54 ± 7 days during December and January, before hatching in mid- to late January. The fledglings left in late April-early May after spending an average 101 ± 0.9 days in the burrow. A logistic growth model, fitted to weekly measurements of skeletal body components, determined that the head, bill and tarsus grew rapidly during early burrow life, while growth of the wing was slow initially and remained incomplete at fledging. Breeding success was measured as 40% and 53% for two successive seasons, and was greater from burrows on a medium gradient than those on slighter gradients in both seasons. Although baseline data are provided here, longer term studies addressing specific demographic parameters, such as adult survival, juvenile recruitment and fecundity, are needed to assess the population status and guide management actions.