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Revista de biología marina y oceanografía

On-line version ISSN 0718-1957

Rev. biol. mar. oceanogr. vol.48 no.3 Valparaíso Dec. 2013

http://dx.doi.org/10.4067/S0718-19572013000300018 

 

NOTA CIENTÍFICA

A population estimate of the Sooty Shearwater Puffinus griseus in the Wollaston and Hermite Island Groups, Cape Horn Archipelago, Chile, and concerns over conservation in the area

Estimación poblacional de fardela negra Puffinus griseus en Islas del Grupo Wollaston y Hermite, Archipiélago Cabo de Hornos, Chile y consideraciones para la conservación del área

 

R. Paul Scofield1,2 and Ronnie Reyes-Arriagada3

1Zoology Department, University of Otago, Box 56, Dunedin, New Zealand
2Present address: Canterbury Museum, Rolleston Avenue, Christchurch, New Zealand
3Instituto de Ciencias Marinas y Limnológicas, Facultad de Ciencias, Universidad Austral de Chile, Casilla 567, Valdivia, Chile. ronnie.reyes@uach.cl


ABSTRACT

We documented the population size of Sooty Shearwater on the Wollaston and Hermite Island Groups. A population of at least 100,000 pairs were found on Wollaston and there may be as many as 300,000 pairs in the Wollaston and Hermite Island Groups. We also confirmed the presence of Magellanic Diving-petrel and Fuegian Storm-petrel in the Island Group and discussed the status of these taxa in southern Chile. The status of the mammals found on these islands is also summarised and concerns are raised over the possibility that introduced mammals, especially beavers, muskrats, minks and feral cats may reach these pristine islands affecting seabird populations.

Key words: Cape Horn, Pelecanoides magellani, Oceanites oceanicus chilensis, introduced species


INTRODUCTION

Recent studies have reported significant declines in the Sooty Shearwater Puffinus griseus (Gmelin, 1789) populations, not only at their New Zealand breeding grounds (Scott et al. 2008) but also on migration (Scofield & Christie 2002) and at their non-breeding grounds (Veit et al. 1997). The status of seabirds on the Tierra del Fuego islands in southern Chile and Argentina are poorly known (Schlatter 1984). In the past 20 years work has been done on terrestrial birds (e.g., Venegas 1981, 1991) of the area but little has been published on seabirds since the 1930s. The discovery of a huge Rockhopper Penguin colony (Eudyptes chrysocome Forster, 1781) on Staten Island (Schiavini 2000), together with large colonies of Black-browed Albatross (Thalassarche melanophris Temminck, 1828) on Noir Island (Clark et al. 1984a) suggests that more is still to be discovered on these remote islands.

Sooty shearwaters breeding colonies were first confirmed on the southern uplands of Wollaston Island in December 1915 (Beck 1918). At the end of 1932 the species was recorded breeding and considered to be exceedingly common on Wollaston and Bayly Islands (Reynolds 1935). Following a gap of ~50 years, Clark et al. (1992) found Sooty Shearwaters breeding on Ildefonso Island, Hornos, Wollaston and Sesambre Islands in 1984 and 1985. Outside the Cape Horn group, Clark et al. (1984b) found a very large colony of Sooty Shearwaters on Guafo Island (43°36'S, 74°43'W) and a smaller colony in the Guamblin Island (44°51'S, 75°5'W) (Clark et al. 1984a, Reyes-Arriagada et al. 2007).

Here we document the population size of Sooty Shearwater on the Wollaston and Hermite Island Groups. Due to the scarce amount of information existing for the Magellanic Diving-petrel Pelecanoides magellani (Mathews, 1912) and the Fuegian Storm-petrel Oceanites oceanicus chilensis (Murphy, 1936), two endemic small petrel taxa of this area, we also briefly summarize what is known about their distribution and biology.

 

MATERIALS AND METHODS

Study sites

The Wollaston and Hermite Groups consist of 10 large islands and 30 small stacks with a total area of 65,000 ha (Fig. 1). On 18th and 19th December 2000 we visited 2 of the 10 islands: Wollaston Island and Epave Island, and made remote observations of Middle Island. Wollaston Island (55°43'S, 67°22'W) is the largest island in the group (673 m, 21,440 ha), primarily vegetated with Magellanic moorland with stands of evergreen Nothofagus betuloides (Mirb.) Oerst. Montane cushion communities predominate above 300 m. Middle Island (26 ha, < 150 m, 55°36'S, 67°19'W) is situated less than 500 m offshore at the south end of Middle Cove on Wollaston Island. This island has forest vegetation similar to Wollaston Island. Epave Island (60 ha, < 50 m A.S.L., 55°49'S, 67°22'W) is in the Franklin Channel that separates Wollaston and Hermite Islands. It is primarily vegetated by Magellanic moorland with a small area of stunted N. betuloides forest on the south and eastern-sides.

 

Figure 1. Location of Wollaston and Hermite Island Groups, Cape Horn Archipelago, Chile

Figura 1. Ubicación de las islas del Grupo Wollaston y Hermite, Archipiélago Cabo de Hornos, Chile

 

Density of burrows of Sooty Shearwater

During this study, a total of 198 10 x 10 m2 quadrats were placed randomly and examined through areas of forest on Wollaston Island, counting all the burrows found. To estimate the area of the colony, the distribution of forest in the Wollaston Island Group was taken from a satellite photograph taken in 1996 (Source: Canada Centre for Remote Sensing of the Canadian Space Agency). Estimates are presented as mean ± SD. Occupancy was assessed by recording faeces, signs of digging and by using smell. We also used long sticks stuck into the burrows to feel birds and also put our hands down the burrow to grab and remove the occupant.

 

RESULTS AND DISCUSSION

Population estimates of Sooty Shearwater

Large numbers of burrows were found in the small stunted N. betuloides forests between 100 and 300 m A.S.L. on Wollaston Island. The density of burrows in the forest was estimated to be 0.105 ± 0.189 burrows m-2. Although the bulk of the island is not covered by forest but Magellanic moorland, we estimated that the area surveyed was 4998 ha (or 23% of the island) and contained 568 ha of suitable forest above 100 m. Thus, we estimate that this area contained about 59,000 burrows. We estimated that 60% of burrows found were in use during the period of the census or had been prospected during the spring of 2000. However only 4 of 150 burrows examined were occupied during the day. This is probably as our visit coincided with the species `honeymoon' period when most breeding birds are away from the island (Warham 1990). If we assume that each of the used burrows was laid in (shortly after our visit), there would be about 35,500 breeding pairs of sooty shearwater in the study area. This estimate is supported by the fact that in the late evening hundreds of birds were seen flying over the inland.

Sooty shearwaters are documented as breeding at forested sites on the southern half of Wollaston Island (Beck 1918, Reynolds 1935, Clark et al. 1992), thus we suggest that the density of burrows as reported for this location is similar elsewhere on the island. Satellite photographs enable us to estimate that approximately 1600 ha of forest exists on Wollaston Island above 100 m. Thus we estimate that approximately 166,500 Sooty Shearwater burrows exist on Wollaston Island. With a 60% occupancy rate based on estimates using signs of occupancy we estimate that approximately 100,000 breeding pairs may be present above 100 m. There may be a small number of shearwaters breeding below 100 m (Reynolds 1935), but none were found during this survey.

On Epave Island, recently occupied Sooty Shearwaters burrows were found on the eastern side of the island below 100 m, whereas occupied burrows of Fueguian Storm-Petrel were found in the cushion plants (Table 1) near sea level and may occur all the way to the summit. Burrows containing light blue feathers that almost certainly belonged to Blue Petrel Halobaena caerulea (Gmelin, 1789) were also found. Unoccupied burrows of Magellanic Diving-petrel recognised by the reddish faeces at the entrance and the presence of two primaries feathers found outside one burrow were found in thick Hebe elliptica (Forster) on the southwest corner of the island.

 

Table 1. The status of procellarids Seabirds on the Wollaston and Hermite Island Groups

Tabla 1. Estado de aves marinas proceláridas en islas del Grupo Wollaston y Hermite

 

The Wollaston and Hermite Island Groups make up 65,000 ha and the Cape Horn National Park is 63,093 ha. We estimate these islands contain about 4800 ha of suitable forest over 100 m. We consider it likely that Sooty Shearwaters occupy all suitable habitats on all islands of the Wollaston Group. If the density and occupancy of burrows is similar on all islands in the group to that on the northern part of Wollaston Island we estimate approximately 300,000 pairs breed in the Wollaston Group.

 

Status of the two endemic breeding petrels of Southern Chile

Both the Magellanic Diving-petrel and the Fuegian Storm-petrel are common in many places in the fjords. However, their breeding habits are poorly known due to the scattered and cryptic nature of their burrows. Outside Wollaston Group (Table 1), records of Magellanic Diving-petrel breeding are only confirmed on a small island south of Puerto Toro, Navarino Island (Reynolds 1935), with specimen records from islands west of the Cockburn Channel, London Island, Islet Antonio in Trinidad Channel (Murphy 1936). The status of Fuegian Storm-petrel has recently been reaffirmed by Palma et al. (2012). Outside Wollaston Group (Table 1), possible breeding sites are on Chanticler, Hoste and Ildefonso Islands (Reynolds 1935, Murphy 1936). There are some records from Gable Island in the Beagle Channel (Oustalet 1891) and Morton Island (Roberts 1940).

 

Introduced mammals of the Wollaston Archipelago

Non-native mammal species were recently introduced to the Wollaston Archipelago (Table 2). Brown Rat [Rattus rattus (Linnaeus, 1758)] and House Mouse (Mus musculus Linnaeus, 1758) have only been recorded from the Wollaston and Hermite Groups since 19781. American mink [Mustela vison (Schreber, 1777)] and muskrat [Ondatra zibethicus (Linnaeus, 1766)] have recently spread to Navarino and Hoste Island (Anderson et al. 2006, Valenzuela et al. 2013a, b; 2014) and mink to Lennox Islands (Davis et al. 2012). Their potential to colonize new areas, in our opinion, makes both species the most significant threat for seabirds in the Wollaston and Hermite Island Groups through predation and/or competition with native species.

 

Table 2. List of native mammal species found and mammal species that could potentially be introduced to the Wollaston and Hermite Island Groups

Tabla 2. Lista de especies de mamíferos nativos encontrados y especies de mamíferos que pueden potencialmente ser introducidos en Islas del Grupo Wollaston y Hermite

 

Domestic dogs were present at the naval base at Ross Cove and Hornos Island during the field work. The faeces of these individuals contained murid fur and Magellanic penguin feathers. The impact of these predators on other seabird species is unknown. Domesticated cats are kept in military outposts and ranches throughout the archipelago and on Navarino Island (Anderson et al. 2006) and may cause a significant impact to seabird populations through predation (Warham 1990). North American Beavers (Castor canadensis Kuhl, 1820) have also spread to Navarino, Hoste, Nueva, Picton and Lennox Island since the 1940's (Anderson et al. 2006). Beaver's self-introduction to the Cape Horn Islands would severely impact the forest community through habitat destruction.

 

Concern for the conservation status of the Wollaston and Hermite Island Groups

These islands have a remarkable and virtually pristine flora and fauna. It is of concern that the introduced mammals, in particular beavers, minks, feral cats and rats may invade these unique sanctuaries. We recommend that the Chilean Government should give and enforce National Park status to these islands. This would help to prevent illegal landings and allow monitoring of the islands, and also in the preparation of contingency plans against the invasion or introduction of unwanted predators.

 

ACKNOWLEDGMENTS

We thank the Armada de Chile and especially the officers and crew of the Patrol Vessel «Mikalvi» and the staff of the Local Maritime Authority Islas Wollaston, Ross Cove for their hospitality. We thank Sgto. Gutiérrez from Local Maritime Authority Cabo de Hornos, Sgto. Retamal from Local Maritime Authority Islas Wollaston, geologist Charles Porter and explorer Cristian Donoso, for recent information about presence of native and introduced mammals on the Archipelago. We thank Alejandro Valenzuela for giving us information concerning impacts of Chilean mammals on seabirds. This research was made possible through a grant from the New Zealand Vice-chancellors Committee's Claude McCarthy Fellowship fund. Work was carried out with the support of the Corporación Nacional Forestal, CONAF (permit 16/02, 2000).

 

NOTE

1Charles Porter and Cristian Donoso, personal communication

 

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Received 27 November 2012 and accepted 22 July 2013
Associate Editor: Maritza Sepúlveda M.