On Christmas Island
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Baiting effectiveness for introduced rats (Rattus sp.) on Christmas Island Andrea Coddou Alvarez (21104982) This thesis is submitted to fulfill the requirements for a Master of Science (Zoology) by way of Thesis and Coursework Faculty of Natural and Agricultural Sciences The University of Western Australia 2012 Supervisors: Dr Harriet Mills (School of Animal Biology, UWA) Dr David Algar (Science Division, Woodvale Research, DEC) This article has been formatted according to the style of the Wildlife Research journal. Acknowledgments I would like to thank my supervisors Dr. Harriet Mills and Dr. Dave Algar for their help and guidance in carrying out this project. Special thanks to Neil Hamilton from DEC who taught me and helped me with the practical part of the project while on Christmas Island. Thanks also in general to the Department of Environment and Conservation for making this project possible by funding and providing working material. I would also like to thank the staff of Christmas Island National Parks for their support and assistance and for lending me their laboratory and materials to work on my project as well as for providing some GPS maps. Special thanks to Joy Wickenden for her support and hospitality and the staff of Christmas Island Phosphates for their help while on the island. Finally I would like to thank Sergio Galdames for his patience and guidance with the statistical analysis of this project. Table of Contents List of Figures…...…………………………………………………………………….….. 1 List of Tables………………….…………...……………………………………….…….. 2 Abstract…………………………………………………………………………………… 3 Introduction………………………………………………………………………………. 3 Methodology……………………………………………………………………………… 7 Results…………………………………………………………………………………...... 12 Discussion………………………………………………………………………………… 15 References………………………………………………………………………………… 19 Literature Review………………………………………………………………………..... 24 Appendix………………………………………………………………………………..… 44 List of Figures Figure 1: Map of Christmas Island showing location and distances to mainland Australia………………………………………………………………….………………... 7 Figure 2: Christmas Island showing an enhanced detail of the north-east corner of the island, where both study sites are located…………………………………….……….…… 8 Figure 3: Collage picture showing the methodology use in this project………..…….…... 10 Figure 4: Percentage of survivorship of radio-collared rats in baited areas…….…….…... 13 1 List of Tables Table 1: Bait efficacy for each site and total bait efficacy……………………...………… 12 Table 2: Mean consumption (g) per bait station…………………..……………………… 14 Table 3: Mean consumption (g) per bait station through time…………………………..... 15 2 Abstract Context. The importance of oceanic islands in terms of conservation of native species is often affected by the introduction of invasive species. Introduced mammalian predators such as feral cats (Felis catus) and rats (Rattus sp.), have been responsible for population decline and extinction of many native species on oceanic islands worldwide. Christmas Island, located in the Indian Ocean, is an example of how introduced mammals have influenced the population of endemic species even to the point of extinction. Aims. The aim was to monitor the effect of a baiting program for rats as part of the management plan for feral cats and rats conducted on the island since 2010 by the Department of Environment and Conservation. Methods. Twenty rats (ten in each site) were trapped in two study sites (Settlement and Upper Poon Saan). Rats were radio collared and released, and then bait stations were opened containing Racumin paste sprayed with coconut milk as an additive. Key results. The baiting had a mean efficacy of 76.5%, with a significant difference (χ2 = 4.650, 1df, P=0.031) observed between the sites (100% at Settlement area and 55.55% at Upper Poon Saan). The mean time of action for the baits for both sites was 5.6 ± 0.6 days and the total mean bait consumption per bait station was 41.6 ± 9.07 g. Conclusions. The results of this study suggest that the type of bait currently in use is adequate but the bait spacing may not be sufficient to control rats successfully on Christmas Island. Implications. It is recommended to place the bait stations without bait in advance so the structure looks familiar to rats in order to avoid bait shyness. It is also recommended to clean up and to remove the rubbish in order to reduce the habitat for rats to aid the control program. Introduction Predation by introduced mammals has affected many native species on oceanic islands worldwide (Sax and Gaines 2008), resulting in a rapid decline of their population and, in 3 some cases, extinction (Courchamp et al. 1999; Blackburn et al. 2004; Harris 2009). It has been documented that human-caused introduction of predators, such as feral cats (Felis catus) and rats (Rattus sp.) has had a major impact on the populations of seabirds, small mammals and other vertebrate species on oceanic islands around the world (Blackburn et al. 2004; Fukami et al. 2006; Harris 2009). Introduced rodents are present on almost every island in the world and they are responsible for the extinction of a high number of species (Rodriguez et al. 2006; Howald et al. 2007). Their ecological success has been largely attributed to their wide-ranging diet, small size and propensity to breed (Kay and Hoeskstra 2008). The primary food source for rats is plant material, but they will also consume other food sources that are most readily available (Taylor et al. 2000; Major et al. 2007; Caut et al. 2008). Some studies reported that rats consume eggs and chicks of breeding seabirds and also adults (Courchamp et al. 1999; Le Corre 2008) as well as reptiles (Caut et al. 2008; Beeton et al. 2010). Christmas Island, a tropical island located in the Indian Ocean (10.4833˚S, 105.6333˚E) approximately 2600 km northwest of Perth and 360 km south of Jakarta (Algar and Johnston 2010), is home to an unusual fauna that has been threatened since the introduction of exotic mammals (Wyatt et al. 2008). Two of the five native mammals of Christmas Island, the bulldog rat (Rattus nativitatis) and Maclear’s rat (Rattus macleari), have become extinct since the arrival of humans and their commensals over a hundred years ago (Armstrong 1992; Wyatt et al. 2008; Harris 2009). The Christmas Island shrew (Crocidura attenuata trichura), originally common on the island, is now critically endangered but is believed by most to be extinct as there have been no confirmed sightings since 1985 (Schulz 2004; Beeton et al. 2010). The population of the Christmas Island pipistrelle (Pipistrellus murrayi) has declined markedly and is now classified as critically endangered and believed to be extinct (Schulz and Lumsden 2004). Introduced mammals also have had a major impact on seabirds of the island such as the Christmas Island frigatebird (Fregata andrewsi), which is listed as vulnerable (Hill and Dunn 2004; DSEWPC 2010). Cats and possibly rats have also had a major impact in the breeding success of red-tailed tropicbird (Phaethon rubricauda) and it is also believed they predate on white-tailed tropicbirds 4 (Phaethon lepturus) as well (Beeton et al. 2010). All four species of land birds that are endemic to the island including the Christmas Island thrush (Turdus poliocephalus erythropleurus), the Christmas Island hawk-owl (Ninox natalis; listed vulnerable), the Christmas Island goshawk (Accipiter fasciatus natalis; listed endangered) and the Christmas Island emerald dove (Chalcophaps indica natalis) (DSEWPC 2012) are considered to be threatened, possibly because of cat and rat predation (Hill 2004a; Hill 2004b; Beeton et al. 2010). According to the Department of Sustainability, Environment, Water, Populations and Community (DSEWPC 2012), there has also been a marked decline of reptile species over the past years. Cats and rats are considered to impact potentially all native species of reptiles on the island (Beeton et al. 2010). The eradication of introduced predators is essential for the recovery and management of declining native species, especially on oceanic islands (Taylor et al. 2000; Ratcliffe et al. 2009; Smith et al, 2009). Restoration programs cannot be limited merely to eradication. It is necessary to conduct pre-eradication assessment as well long-term post-eradication monitoring (Courchamp et al. 2003). A good management plan for introduced predators has to consider the value of long-term ecological monitoring of both superpredator and mesopredator (Rayner et al. 2007; Russell et al. 2008). Several eradication programs for introduced mammals have been implemented on oceanic islands worldwide over the past years (Howald et al. 2007). Selective poisoning is the most widely used method of eradicating introduced rodents on smaller islands, while on larger islands eradication becomes a high-risk operation due to the necessity for aerial dispersion of bait and thus the high probability of poisoning non-target species (Taylor et al. 2000; Howald et al. 2007, Harris 2009). Some methods to avoid poisoning non-target species include the selection of bait type and the use of bait stations (Howald et al. 2007) because these are less accessible to non-target species than baits on the ground. The choice of rodenticide must be balanced between efficacy and the risks to non-target species (Donlan et al. 2003). Additives can increase the rodent consumption of the toxin by making the bait more palatable and therefore may improve the results of the eradication program. Some additives used to increase palatability of baits include