BreedingofCory's shearwater Calonectris borealison Selvagem Grande and beneficial effects of removal of invasive mammals
F. ZIN O,
M.BIS C O I T O and A. BUCKLE
Abstract The largest colony of Cory’s shearwater Calonectris borealis nests on the island of Selvagem Grande in the north-eastern Atlantic. In 2002,a pro- gramme of eradication was conducted to remove two alien invasive mammals, the house mouse Mus musculus and European rabbit Oryctolagus
cuniculus.Preliminary studies recorded beneficial effects of the eradications for a variety of plant and animal species, including Cory’s shearwater. We recorded fledging rates of shearwaters for 1982–2001, prior to the eradication, and for 2002–2020, after the eradication, from two quadrats, each containing 134–329 nest sites. Although there was annual fluctuation in fledging rates in the quadrats, the mean rate of 40.74 ± SD 3.92 fledglings per 100 nest sites for the two quadrats combined prior to the eradication of mammals increased significantly, to 52.88 ± SD 5.03 per 100 nest sites, after the eradications. Because the two mammals were removed synchronously it is difficult to know which factors de- pressed fledging of Cory’sshearwatersonSelvagem Grande. However, the predatory behaviour of house mice on other oceanic islands, and the fact that increased fledg- ing was seen soon after the eradications occurred, suggest predation by house mice on shearwater hatchlings was the main cause of losses.
Keywords Alien invasive species, Calonectris borealis, Cory’s shearwater, European rabbit, house mouse, Mus musculus, Oryctolagus cuniculus, Selvagem Grande
Introduction T
he Cory’s shearwater Calonectris borealis colony on the Portuguese island of Selvagem Grande has been the
subject of study since the first scientific expedition to the island in 1963 (Pickering & Maul, 1965). Although catego- rized on the IUCN Red List as Least Concern (BirdLife
F. ZINO (Corresponding author,
orcid.org/0000-0001-9309-0786)
Freira Conservation Project, Rua Dr. Pita 7, 9000-089 Funchal, Madeira, Portugal. E-mail
fzino@netmadeira.com
M. BISCOITO (
orcid.org/0000-0002-9347-0823) Museu de História Natural do Funchal, Madeira, Portugal
A. BUCKLE (
orcid.org/0000-0002-5449-9279) School of Biological Sciences, The University of Reading, Reading, UK
Received 19 January 2021. Revision requested 6 April 2021. Accepted 5 May 2021. First published online 28 October 2021.
International, 2018), Cory’s shearwater is a Species of European Conservation Concern, category 2 (concentrated in Europe) with a threat status of depleted (BirdLife International, 2017). The Selvagem Grande population has been estimated to be 29,450 breeding pairs and therefore comprises the largest breeding colony of this seabird (Granadeiro et al., 2006). This is considerably less than the 130,000–150,000 breeding pairs formerly believed to have bred on the island (Mougin &Mougin, 2000). The de- clinewas caused by intensive culling of chicks and adults for meat, oil and feathers by local fishermen (Zino, 1985). To halt this culling, Paul A. Zino (father of FZ) bought the cul- ling rights in 1967 and built a small house on the island to support scientific study. This effectively turned the island into a wardened private nature reserve until it was made an official Nature Reserve by the Portuguese government in 1971, but wardening ceased and illegal killing resumed, with the indiscriminate slaughter in 1976 resulting in an estimated 8,000 breeding pairs in 1980 (Zino, 1985). Since 1981, Selvagem Grande has been wardened byMadeiran in- stitutions, including latterly the Instituto das Florestas e Conservação da Natureza (previously Parque Natural da Madeira). This has resulted in an increase in the population of Cory’s shearwaters of c. 5%per annum (Granadeiro et al., 2006). The breeding biology of Cory’s shearwater on Selvagem
Grande is well studied (Zino, 1971; Zino et al., 1987, 1991; Mougin & Jouanin, 1997; Mougin, 2000; Mougin et al., 2000; Mougin & Mougin, 2000) and the breeding cycle is consistent from year to year. Birds start to return to the is- land in early February, with numbers increasing through to March. Mating occurs mainly in April and egg-laying during late May–mid June (Zino et al., 1987; Thibault et al., 1997). Immediately after the female lays the single egg, the male takes over incubation but thereafter they incu- bate alternately. Incubation is 54 days and eggs hatch mid July–early August (Zino, 1971; Zino et al., 1987). Parent birds remain at the nest for 3–4 days after hatching, leaving chicks at risk of predation thereafter by the Madeiran wall lizard Teira dugesii selvagensis (Matias et al., 2009), yellow- legged gull Larus michahellis and, formerly, house mice Mus musculus (F. Zino, pers. obs., 1963–2008). Adults make long journeys, as far as the coast ofMauritania (F. Zino, unpubl. data, 1996), to obtain food for their young. Chicks reach maximum weight in September, which is when culling pre- viously occurred, some reaching almost double their adult
This is an Open Access article, distributed under the terms of the Creative Commons Attribution licence (
http://creativecommons.org/licenses/by/4.0/), which permits unrestricted re-use, distribution, and reproduction in any medium, provided the original work is properly cited. Oryx, 2022, 56(6), 927–934 © The Author(s), 2021. Published by Cambridge University Press on behalf of Fauna & Flora International doi:10.1017/S0030605321000661
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