Birds of Enderby Island, Auckland Islands, New Zealand Subantarctic
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4 Birds of Enderby Island, Auckland Islands, New Zealand subantarctic REBECCA K. FRENCH* RODNEY B. RUSS Charles Perkins Centre, School of Life and Strannik Ocean Voyages, PO Box 9172, Environmental Sciences and Sydney Medical School, Christchurch 8011, New Zealand The University of Sydney, Sydney, NSW 2006, Australia GRAEME A. TAYLOR COLIN M. MISKELLY Department of Conservation, PO Box 10420, Museum of New Zealand Te Papa Tongarewa, Wellington 6011, New Zealand PO Box 467, Wellington 6140, New Zealand ALAN J.D. TENNYSON CHRIS G. MULLER Museum of New Zealand Te Papa Tongarewa, Wildbase, School of Veterinary Science, PO Box 467, Wellington 6140, New Zealand Massey University, Palmerston North 4442, New Zealand ABSTRACT: Enderby Island is a much-visited small island in the New Zealand subantarctic, and is an important area for birdlife. However, despite this, the bird community of Enderby Island has never been systematically described. We summarise bird records on Enderby Island from 1840 to 2018. Using these data we describe the bird community with an emphasis on resident species, and compare the frequency of sightings before and after eradication of invasive mammals in 1993. We also investigate trends in bird sightings from 1992 to 2018. There was a significant increase in the sightings of some species, including tui (Prosthemadera novaeseelandiae) and silvereye (Zosterops lateralis), and a significant decrease in others, including white-fronted tern (Sterna striata). Some species, such as New Zealand falcon (Falco novaeseelandiae) and Auckland Island snipe (Coenocorypha aucklandica aucklandica), have recovered successfully following dramatic historical declines. We hypothesise that these trends in sightings are driven by changes in human exploitation, the introduction and subsequent eradication of browsing mammals and mice, changes in the abundance and structure of the invertebrate community, and changes in vegetation cover. However, we believe that trends in sighting rates of southern royal albatross (Diomedea epomophora) may be an artefact of changes in visitor behaviour following the construction of a boardwalk, rather than changes in the species’ abundance. French, R.K.; Miskelly, C.M.; Muller, C.G.; Russ, R.B.; Taylor, G.A.; Tennyson, A.J.D. 2020. Birds of Enderby Island, Auckland Islands, New Zealand subantarctic. Notornis 67(1): 189–212. KEYWORDS: Auckland Islands, Enderby Island, subantarctic, New Zealand, population ecology, biogeography Received 24 May 2019; accepted 22 June 2019 *Correspondence: [email protected] Introduction thick scrub. The centre of the island consists primarily of low herbs and cushion plants, Enderby Island (50°30’S, 166°17’E) is part of the interspersed with small gullies of scrub. The Auckland Island archipelago, and is situated to northern and western sides of the island are the north-east of the main Auckland Island, in the much more exposed to weather and ocean New Zealand subantarctic. The island is relatively spray, and are primarily covered in tussock (Poa small (695 ha), comprising approximately 1% of litorosa). Close to the northern cliffs, only salt- and the total land area of the Auckland islands (R.H. wind-tolerant plants such as Bulbinella rossii and Taylor 1971; Torr 2002). It has a fairly flat topog- Anisotome latifolia appear to be able to grow. To raphy and low elevation, rising only 45 m above the south there is a large bay with a sandy beach sea level. This is much lower than Auckland Island (Sandy Bay), and above the beach a sward area (with a maximum elevation of 659 m), and Adams with short lawn-like vegetation. This is thought Island (705 m). Due to its position and low eleva- to be the result of human-induced fire and of tion, the climate also differs from that of the other browsing by introduced mammals (R.H. Taylor Auckland Islands, with less rainfall and higher 1971; Torr 2002). Pigs were released in 1807 and average temperatures (de Lisle 1965; Higham 1991). 1867, rabbits in 1865, and cattle in 1894, and mice Southern rātā (Metrosideros umbellata) forest were accidentally introduced probably before covers the southern and eastern sides of the 1840 (R.H. Taylor 1971; Russell et al. 2020 – Chapter island (Fig. 1). Closer to the interior are areas of 6 in this book). These species were all eradicated 190 FIGURE 1. Map of Enderby Island showing sites mentioned in text in white. Vegetation types are in black. South-west Point is also known as Rapoka Point, North-east Cliffs as Fur Seal Cliffs, and South-east Point as Pebble Point. The Department of Conservation hut (near Sandy Bay) is marked with a hut symbol, and the boardwalk with a dotted line. Adapted from image provided by Dave Houston. Birds of Enderby Island in 1993, with the exception of pigs, which had (Phocarctos hookeri) researchers have occupied already died out (Torr 2002; Russell et al. 2020 – the island almost annually over the summer Chapter 6). months. During this period, the researchers mon- Enderby Island is considered an important itored southern royal albatross (Diomedea epomo- breeding area for several species and subspe- phora) nest numbers (Childerhouse et al. 2003; cies endemic to the Auckland Islands, including Baker et al. 2020 – Chapter 10 in this book) and the Auckland Island shag (Leucocarbo colensoi), undertook yellow-eyed penguin beach counts Auckland Island snipe (Coenocorypha auck- (Chilvers 2014; Muller et al. 2020 – Chapter 9), landica aucklandica), Auckland Island teal (Anas as well as making other sporadic wildlife obser- aucklandica), Auckland Island banded dotterel vations. Enderby Island has also been a key site (Charadrius bicinctus exilis), and Auckland Island for ecotourism in the New Zealand subantarctic. tomtit (Petroica macrocephala marrineri) (BirdLife Heritage Expeditions (an ecotourism company International 2019). It is also a key breeding site that has visited the island every year since 1992) for the yellow-eyed penguin (Megadyptes antipo- compiles a list of bird records from every trip, des) (Muller et al. 2020 – Chapter 9 in this book). which we use in this article to assess recent The entire Auckland Islands archipelago is desig- trends in bird sightings. nated as an Endemic Bird Area (EBA) and world The ecology of Enderby Island has been affected heritage site (BirdLife International 2019), and is by human activities, including the burning of managed as a nature reserve by the New Zealand vegetation and the release of mammalian pests Department of Conservation. (R.H. Taylor 1971). By 1875 there were at least 100 Enderby Island has a rich history of human pigs on Enderby Island (R.H. Taylor 1971). After 127 visitation (Miskelly & Taylor 2020 – Chapter 1 years on Enderby Island, rabbits had an estimated in this book). Māori occupied the island before population size of 5,000–6,000 immediately prior European discovery (Anderson 2005), but the to eradication (Torr 2002; Russell et al. 2020 – island was uninhabited when it was first dis- Chapter 6). These introduced mammals had a 191 covered by Europeans in 1806 (R.H Taylor 1971; large effect on the ecology of the island, confining Miskelly & Taylor 2020 – Chapter 1). Scientific vulnerable plants such as Stilbocarpa polaris and exploration of the Port Ross area began with Anisotome latifolia to cliff edges, and replacing visits of ships from the United States, France, tussock areas (which were almost eliminated) and the United Kingdom in 1840, and a German with cropped sward (Challies 1975; R.H. Taylor 1975; expedition to observe the transit of Venus in Torr 2002; Russell et al. 2020 – Chapter 6). The lack 1874 (Fraser 1986; Jones 2009). Much new infor- of vegetation cover is likely to have made species mation was gathered almost 70 years later, when such as the Auckland Island snipe more vulnerable military personnel (equipped with small boats) to avian predators, including subantarctic skua were posted at nearby Ranui Cove during the (Catharacta antarctica lonnbergi) and New Zealand Second World War ‘Cape Expedition’ (Miskelly falcon (Falco novaeseelandiae) (Torr 2002). & Taylor 2020 – Chapter 1). Personnel included Mice were thought to have a large impact on experienced ornithologists, who produced for the invertebrates, which are an important part of the first time a description of the bird community on diet of native birds such as the snipe and tomtit Enderby Island (Turbott 2002). (Torr 2002). Following the war, there were several scientif- Despite the island’s ecological importance, long ic expeditions in the 1950s through to the 1980s, history of visitation, and invasive mammal eradi- including Dominion Museum and Department of cation, the bird community of Enderby Island has Scientific and Industrial Research (DSIR) expe- never been described in detail. In this study, we ditions in 1954, 1962-63, and 1966 led by Robert describe the bird communities on Enderby Island Falla, a 1972-73 expedition led by Brian Bell, and using records from 1840 to 2018, with an emphasis a broad ornithological survey in 1988 by Graeme on resident species. We compare the frequency of Taylor (Wodzicki & Taylor 1955; Bell 1963; Falla sightings before and after the invasive mammal 1975a; G.A. Taylor 1988; Miskelly & Taylor 2020 eradications in 1993, and investigate trends in bird – Chapter 1). Since 1975, New Zealand sea lion sightings from 1992 to 2018. Lost Gold: ornithology of the subantarctic Auckland Islands Materials and methods grouped into time periods with a similar number of lists for comparison (Table 1). A database of bird sightings on Enderby Island 2. We studied recent trends in bird sightings using was collated. A detailed description of the colla- the data collected by Heritage Expeditions from tion methods and sources of information (includ- 1992 to 2018. For each year, the number of times ing abbreviations for observers) can be found a bird species was noted as present was divided in Miskelly et al. (2020 – Chapter 2 in this book, by the total number of voyages conducted and see Supplementary materials http://notornis.