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DISTRIBUTION, BREEDING AND STATUS OF THE STRIATED CARACARA PHALCOBOENUS AUSTRALIS (GMELIN, 1788) IN SOUTHERN CHILE DISTRIBUCIÓN, NIDIFICACIÓN Y ESTATUS DEL CARANCHO NEGRO PHALCOBOENUS AUSTRALIS (GMELIN, 1788) EN EL SUR DE CHILE

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Abstract and Figures

The genus Phalcoboenus of caracaras is a New World group that is comprised of four medium size species, mainly scavenger birds of prey. The four species are linked mainly to vegetation free zone along the Andean-patagonian axis, from Ecuador south to the southern end of South America (Vuilleumier 1970, 1991). The Striated Caracara (Phalcoboenus australis) has been considered a rare and near-threatened species, very local or with unknown status, inhabiting the southern islands of extreme southern South America, including the Falklands Islands (or Islas Malvinas), and as a casual visitor to the southern and southeastern coast of the Isla Grande de Tierra del Fuego (Blake 1977, Collar 1986, Jaksic & Jiménez 1986, del Hoyo et al. 1994). Here we present new information on distribution, breeding and status of this species in Chile.
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Anales Instituto Patagonia (Chile), 2006. 34: 65-74
DISTRIBUTION, BREEDING AND STATUS OF THE STRIATED CARACARA
PHALCOBOENUS AUSTRALIS (GMELIN, 1788) IN SOUTHERN CHILE
DISTRIBUCIÓN, NIDIFICACIÓN Y ESTATUS DEL CARANCHO NEGRO
PHALCOBOENUS AUSTRALIS (GMELIN, 1788) EN EL SUR DE CHILE
Manuel Marín
1, 3
, Alejandro Kusch
2,3
, David Oehler
3
& Scott Drieschman
3,4
ANTECEDENTS
The genus Phalcoboenus of caracaras is
a New World group that is comprised of four me-
dium size species, mainly scavenger birds of prey.
The four species are linked mainly to vegetation
free zone along the Andean-patagonian axis, from
Ecuador south to the southern end of South America
(Vuilleumier 1970, 1991). The Striated Caracara
(Phalcoboenus australis) has been considered a
rare and near-threatened species, very local or with
unknown status, inhabiting the southern islands of
extreme southern South America, including the
Falklands Islands (or Islas Malvinas), and as a casual
visitor to the southern and southeastern coast of the
Isla Grande de Tierra del Fuego (Blake 1977, Collar
1986, Jaksic & Jiménez 1986, del Hoyo et al. 1994).
Here we present new information on distribution,
breeding and status of this species in Chile.
We review and summarize published ac-
counts, additional information from museum spe-
cimens, and our own personal observations on the
species gathered throughout the southern islands,
channels, and fjords of southern Chile. We include
observations from three cruises between Punta Arenas
and Noir Island, between 11-16 November 2003,
14-21 November 2004 and 8-11 November 2005.
One trip through the exterior islands between Noir,
Recalada and Inman Islands on 12-18 November
2005. Additional observations were made by (MM)
during cruises on board of M/V Terra Australis and
Mare Australis, on 13 different passages between the
strait of Magellan and Beagle Channel, from 2001
through 2003 and dates ranging from December
to April (2001: 27 January to 3 February; 10-17
February; 3-10 March; 10-17 March; 17-24 March;
14-21 April; 1-8 December; 2002: 19-26 January;
9-16 February; 9-16 March; 23-30 March; 2003: 25
January to 1 February; 22 February to 1 March). We
also include observations by (MM) on 24 different
passages between Puerto Montt and Cape Horn
on board of the M/S Nordnorge on dates ranging
from December to February, between 2002-2006.
(2002: 14-19 December; 20-26 December; 2003:
11-16 January; 17-22 January; 9-13 February; 14-
19 February; 13-18 December; 19-25 December;
2004: 11-16 January; 17-22 January; 7-12 February;
13-19 February; 11-16 December; 17-23 December;
2005: 8-14 January; 15-20 January; 5-10 February;
11-16 February; 10-16 December; 17-22 December;
1
Section of Ornithology, Natural History Museum of Los Angeles County, 900 Exposition Boulevard, Los Angeles CA 90007, USA, Current
address: Casilla 15 Melipilla, Chile. mma559@yahoo.es
2
Casilla 19, Punta Arenas, Chile.
3
Feather Link, Inc. 1013 Westchester way, Cincinnati, OH 45244, USA.
4
Wildlife Concepts International, Inc., Grant Pass, OR 97527, USA.
Recibido 28/4/2006 Aceptado 5/5/2006
66
M. MARÍN et al.
2006: 6-13 January; 14-19 January; 3-9 February;
and 10 to 16 February). Observations made during
one cruise by (AK) on board of L. A. M. Austral II
from Punta Arenas south to Cape Horn, between
18 - 24 October 2002. Two cruises made by (AK)
on board of R/R Pto. Edén, from Puerto Natales
to Puerto Montt, between 17-20 and 25-27 No-
vember 2000. We used a Garmin portable GPS
for geographical positions otherwise latitude and
longitude localities were taken from Riso Patron
(1924), Paynter (1988) or navigational charts. The
nomenclature of egg shape follows Preston in Palmer
(1962). Egg measurements were taken with a dial
caliper to the nearest 0.1 mm. Egg masses were
taken with an AVINET 100 g Pesola.
DISTRIBUTION
Historically, the Striated Caracara (Phalco-
boenus australis) apparently was first mentioned for
Chile (sensu Hellmayr & Conover 1949) by Forster
in Darwin, Zoology of the Beagle in 1838. Without
much specific localities, they reported the species
from small islands near Tierra del Fuego, Diego
Ramírez, Ildefonso, etc. Gay (1847) mentioned the
species as occurring in the extreme south of Chile;
his account was based mainly on Darwins accounts
of the Beagle. Hellmayr & Conover (1949) also
reported for Chile a specimen collected by Cassin
in 1858, at Orange Harbour (55°S) (Hoste Is.) and
“Tierra del Fuego. For localities and geographical
positions, see figure 1 and appendix 1). Curiously, the
Striated Caracara was not included in the Southern
Hemisphere species list Cassin (1855). Most of the
information on the species came from the Falklands
Islands (Malvinas) in the 1930’s and thereafter.
It is worthwhile to mention that Reynolds
(1932) reported a sight record from the Woodcock
Islands (also known as Becasses (55°S)(on Argentinean
territory which is less than 2 km from the Chilean
border) on the Beagle Channel. Hellmayr (1932) on
his publication on Chilean birds did not include the
species, because he did not considered birds from
the far south. Apparently, the next account for the
species on Chilean territory was by Reynolds (1935)
on which breeding was first reported for Chile. He
indicated that a number of birds were breeding on
some of the islands of the Wollaston Archipelago
(55°S), Freycinet, Deceit, and Barnevelt. Nevertheless,
he only mentioned two nests for Barnevelt Island
(see below). The species was not mentioned by Reed
& Philippi (1938) and Housse (1945). The next
account for the species was by Orlog (1948) who
mentioned the sighting of isolated birds in February
on Yendegaia (54°S) and Puerto Navarino (54°S).
On 13 visits to Yendegaia and 7 to Puerto Navarino
between 2001 and 2005, in December, January,
February, March and April, the Striated Caracara
was never observed there, although subadults and
adults of the White-throated Caracara (Phalcoboenus
albogularis) were occasionally present. Later, Orlog
(1950), reported without providing any details the
Striated Caracara for all the islands of the Cape Horn
Archipelago, with a specimen from Herschel Island
(55°S) and breeding on Grevy, Bayly, Freycinet,
and Herschel Island. Goodall et al. (1951) citing
Reynolds, mentioned that species did occur on the
islands south of the Beagle Channel.
According to Philippi (1964), the species
was found in Chile only on the islands south of the
Beagle Channel and the Wollaston and Cape Horn
Fig. 1. Map showing the different localities where the Striated Caracara
have been found in Chile (see also appendix 1 for names and geographical
positions).
67
DISTRIBUCIÓN DEL CARANCHO NEGRO PHALCOBOENUS AUSTRALIS
Archipelagos. Johnson (1965), Meyer De Schauensee
(1970), and Blake (1977) repeated the same infor-
mation. Humphrey et al. (1970) did not add much
new information about the species in Isla Grande
de Tierra del Fuego, in addition to what was already
published, except that it was an uncommon species,
and possibly is a breeding resident along the southern
and northeastern coast of Isla Grande de Tierra del
Fuego. Barros (1976) observed a pair on Nueva Is.
and local people did inform him that the species
breed on the southeastern end of the island.
On the next account, Venegas & Jory
(1979) indicated that the Striated Caracara was
not only restricted to the southernmost islands, as
mentioned by previous authors, but was a relatively
common species along the western outer islands of
the Magellanic region. Venegas & Sielfeld (1979)
mentioned a series of sightings for this species along
the coastal islands of the XII Region, and found four
birds at Vorposten islands (49°S). These islands seem
to be the northernmost sites for the species along
the Chilean coast (see also Appendix 1). They also
reported the observation of 18 birds at Recalada
Island. Venegas (1982) reported but without providing
detailed information, dates, etc., the species breeding
at Diego Ramírez Islands, with a sight record in March
1980, at estancia Consuelo (ca. 50°S), prov. Última
Esperanza. Schlatter & Riveros (1987) reported the
species as resident on the Diego Ramírez, islands but
did not comment further. Wallace (1991) reported
the observation on 23 February 1989, of 15 birds
at Gonzalo Island, one of the islands of the Diego
Ramírez Archipelago. Curiously, during two visits
by MM to Gonzalo Island, on 6 January 2006 and
on 3 February 2006, the species was not observed.
Oddly enough, Clark et al. (1992) writing on the
birds of Cape Horn Islands (55-56°S) mentioned
the species on Guarello Island (50°S).
According to Humphrey et al. (1970), the
Striated Caracara is rare and with uncertain status
on Tierra del Fuego. During our cruises we observed
one or two and up to three birds between 2001 to
2003 and dates ranging from December to April,
on mainland Tierra del Fuego, at Seno Agostini,
prov. Antártica, in an area locally named as “Con-
dor Bay” (54°S). On 24 February 2003, we found
a bird in juvenal plumage at Condor Bay”, which
might indicate breeding on or near the site. If that
were the case it would be the first breeding site on
mainland Tierra del Fuego. In this area, there are
about five to six small colonies (ranging from 5 to
10 pairs) of Rock (Phalacrocorax magellanicus)
and Imperial cormorants (Phalacrocorax atriceps)
and nearby, within ± 2 km a small colony of South
American Sea Lions (Otaria flavescens) those co-
lonies can serve as food sources. Another potential
breeding site observed during those cruises was on
the smallest of the three major and northernmost
islands Tucker (54°S), prov. Tierra del Fuego. On
16 February 2001, we encountered two adults, on
15 April 2001 a single adult, on 19 January 2005,
we encountered two juvenile birds, on 18 January
2006 we encountered a single adult, on 15 Februa-
ry 2006 we encountered two adults, on the same
island. On this island, there is a colony of over 800
pairs Magellanic Penguins (Spheniscus magellani-
cus) about 300 and 50 pairs of Imperial and Rock
cormorants, respectively plus gulls and other birds.
We must mention that during 24 passages between
December and February between Cape Horn and
Puerto Montt, the Striated Caracara was only obser-
ved in four areas, namely: islands Tucker, Solitario,
Terhalten, and Hornos. During two cruises between
Puerto Natales and Puerto Montt in November, it
was not observed. Even though the internal channels
offer several potential sites for the species.
We found very few Chilean specimens
in museums, and most of them with little or no
information. The localities and dates of specimens
are listed in appendix 1. The dates of observations
or collections range from October to April. We did
not find, or have any reliable data for the austral
winter months, although, Couve & Vidal (1998) and
Matus & Barría (1999) mentioned the species as
accidental winter visitor, in Torres del Paine National
Park, but did not provided further information on
it. However, it is likely that, both publications refer
to either or both, Venegas (1982) report [which
was actually on March] at estancia Consuelo, prov.
Última Esperanza; and/or a photo published by
Garay & Guineo (2000)[however, the actual photo
was taken at Laguna Amarga (51°S) in March/April;
O. Guineo pers. com. to AK]. Both records are in
autumn and actually outside of the park limits; as
a consequence, there are no actual winter records
for the area. Jaksic et al. (2002) in a recent review
of the raptors of Torres del Paine National Park do
not mention the species for the park nor referred
68
M. MARÍN et al.
to its potential presence in the area. The species
might make short inland moves but it is primarily
a coastal species. Strange (1996) indicated that, in
some regions of the Falkland Islands (Malvinas),
some Striated Caracaras, particularly immature,
are nomadic and have a post-breeding dispersal
from mid-April to July. Similar behavior should be
expected for Chile, but how far or as to where do
Chilean birds go is unknown.
BREEDING
Gay (1847) mentioned a general account
on the breeding of the species as nesting on small
islands and in rock crevices, but did not specify
nests sites. Gay based his account on Darwin’s
observations during the Beagle voyage. As far as
we know, the only reliable accounts on breeding in
Chile are by Reynolds (1935); that have been repea-
ted by multiple and subsequent authors. Reynolds
mentioned two nests with a single nestling each, in
December. Both nestlings were in a yellow-downy
plumage. He described the nests as being placed in
fissures, crevices, or ledges at the top of perpendi-
cular cliffs, running from the sea. The nests were
similar in shape and form to those of the Crested
Caracara (Caracara plancus), made mainly of bents,
roots, grasses and seaweeds. Although the species
was mentioned as resident by Schlatter & Riveros
(1987) in the Diego Ramírez Archipelago, there
is no mention of nesting or nests in the area. We
found a nest on 12 November 2003 at Noir Island
(Figs. 2 y 3). The nest was located about 3 m from
the ground, in a crevice, in a beach boulder and the
boulder was covered on the top with vegetation. The
nest platform, c. 35 cm in diameter, was made of
fine sticks, and lined with ne, soft and brownish
vegetation. The nest contained 3 eggs, all short
sub-elliptical in shape, cream-colored, overlaid
irregularly from light to heavy, brown and reddish-
brown blotches, covering the entire surface. The
eggs of the Striated Caracara were similar in color
to those of other caracara species. They measured
62.3 x 45.1 mm (63 g), 62.1 x 45.5 mm (60 g),
and 62.3 x 45.3 mm (63.5 g). A second nest was
found on Noir Island on 9 November 2005, clearly
seen with binoculars, the adult bird was sitting on
the nest, and most likely with eggs, but we could not
check the contents. This nest was located among
some live plants on a crevice on a cliff at about 15
m from the ground.
STATUS
In accordance with previous observations
on the species, we mainly observed the Striated
Caracara directly associated with colonial birds or
mammals (see also below). However, the observations
with no association to a colonial bird or mammal,
e.g., Woodcok Island, Agostini Sound, Condor Bay,
Hornos Island, either penguins, cormorants or ma-
rine mammals colonies were within short distance.
The only main exceptions were the two “inland
records at Estancia [Pto.] Consuelo and at Laguna
Amarga, both in prov. Última Esperanza. Along the
Chilean territory, all observations of Striated Cara-
caras involve from one to four birds; exceptionally
large numbers have been reported in association with
Fig. 3. Nest and eggs of Striated Caracara at isla Noir.Fig. 2. Adult Striated Caracara (Phalcoboenus australis).
69
DISTRIBUCIÓN DEL CARANCHO NEGRO PHALCOBOENUS AUSTRALIS
Rockhopper Penguins (Eudyptes chrysolophus) (Clark
1988, Venegas & Soto 1992). The same occurred
on Falkland Islands (Malvinas) (Strange 1996), Sta-
ten Island (Schiavini et al. 1999), Año Nuevo and
Staten Islands (Frere et al. 1999). At Noir Island
the species was mainly observed over and around
Rockhopper Penguin colonies, but also observed
over Macaroni Penguins (Eudyptes chrysocome),
Magellanic Penguins, Imperial Cormorants and Giant
Petrels (Macronectes giganteus) colonies, although
in smaller numbers on the last species. However,
out of 28 observations on different locations, 71%
of the cases were associated with cormorants, 60%
with penguins, 25.5% with marine mammals, 14%
no association and 7% with petrels or albatrosses.
At Condor Bay, Noir and Hershel Islands,
the birds spent a considerable amount of time on
rocks or beaches of the intertidal zone, during low
tide, apparently foraging on mollusks. According
to Strange (1996) the species feed on limpets and
mussels on the Falklands Islands (Malvinas), and
southernmost Chile.
In November 2003, 2004 and 2005, we
found a healthy population of Striated Caracaras on
Noir Island. The maximum number of birds observed
in a single count at one point of the island was 18
individuals (both sub-adults and adult birds). Counts
of 7 to 10 birds at different points of the island were
not uncommon. The population of Noir Island (15.3
km
2
) was in the order of 150 individuals. Similarly, F.
Todd (fide Strange 1996) that visited Noir Island in
November 1984, estimated the population to reach
at least 100 birds. This agree with G. S. Clark (fide
Strange 1996) that visited Noir in February 1984
and found it very common on the island counting
seven at one time. Reynolds (1935) reported 200
birds on Barnevelt Island (55°S) in 1932. However
the largest concentration observed by us was 38
birds in a single count, on 14 November 2005 at
Islote Leonard (53°S). Leonard, is a small island of
500 x 200 m, on Otway Bay, near Recalada Island,
that contains a colony of Imperial Cormorants of
about 400 -500 breeding pairs, several seals, and
penguins. The second largest concentration of
Striated Caracaras was observed at Terhalten Island
(55°S) on 4 February 2006, where 30 birds were
observed on a single count around a colony of Im-
perial Cormorants (ca. over 500 pairs) and next to
a colony of fur seals. We agree with the assertions
of Venegas & Jory (1979) that the species is more
common, particularly farther north, as initially
thought by many authors, e.g., Philippi (1964), Jo-
hnson (1965), Humphrey et al. (1970). Still recent
summaries on Chilean birds e.g., Jaramillo et al.
(2003) have their distributional map off by several
hundred kilometers. However, based on present data,
Striated Caracaras are far more common and their
distribution is farther north than indicated by most
publications. The species should be considered locally
abundant on the outer islands of the XII region of
Chile, most likely north to the southern part of the
Taitao Peninsula. The listing of this species as rare
in Chile, is perhaps a reflection of how infrequent
ornithological surveys are conducted on the outer
islands of southern Chile.
ACKNOWLEDGMENTS
We are grateful to the museum curators and
collection managers for providing data from Striated
Caracara specimens (when the acronims are in pa-
renthesis indicated they had Chilean specimens of
the species): P. Sweet, American Museum of Natural
History (AMNH); John Bates, Field Museum of Natural
History (FMNH); Claudio Venegas, Instituto de la
Patagonia (CZIP); A. Pirie, Museum of Comparative
Zoology at Harvard University; J. Artigas, Museo
Zoología Universidad de Concepción; J. C. Torres-
Mura, Museo Nacional Historia Natural, Santiago;
R. Schlatter, Museo Zoología Universidad Austral
(MZUA); Kimball Garret, Natural History Museum
of Los Angeles County; Gary Graves and James
Dean, United States National Museum; Western
Foundation of Vertebrate Zoology; Kristoff Zyskowski,
Yale Peabody Museum. This work was supported
by Feather Link, Inc. By grants-in-aid for scientific
research from local and international foundations.
We would like to thank Briant Hunt, African Safari
Wildlife, Park and Faunia for their support of this
and past expeditions. Our gratitude must also be
expressed to W. Roger Fry and Leonard Weakly, Jr.
Fortheir Continued support and participation in this
project. We also are grateful to Fanstico Sur Birding,
to the crews of the M/V Terra Australis, M/V Mare
Australis, M/S Nordnorge, L.A.M. Austral II, and
M/V Chonos, for transport to different parts of the
austral seas. We are also grateful to the reviewers
for comments and improving the manuscript.
70
M. MARÍN et al.
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la determinacn de un nuevo distrito zoogeográ-
fico en el litoral exterior de Magallanes. Anales
Instituto Patagonia, (Chile) 10: 201-208.
Venegas, C. & N. Soto 1992. Estudio de pingüinos
eudyptidos en isla Recalada, R.N. Alacalufes,
Chile. Informe final UMAG-CONAF, temporada
1991-1992, Punta Arenas, Chile.
Venegas, C. & W. Sielfeld 1998. Catálogo de los
vertebrados de la región de Magallanes y
Anrtica Chilena. Ed. Univ. Magallanes, Punta
Arenas, Chile.
Vuilleumier, F. 1970. Generic relations and speciation
patterns in the caracaras (Aves: Falconidae).
Breviora 355: 1-29.
Vuilleumier, F. 1991. Especiación en aves de Fuego-
Patagonia Chilena: Estudios preliminares.
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(Chile) 20: 83-88.
Wallace, G.E. 1991. Noteworthy birds records from
southernmost Chile. Condor 93: 175-176.
72
M. MARÍN et al.
Appendix 1. Dates, localities and positions of sightings and specimens of the Striated
Caracara from southern Chile. Localities are ordered from south to north.
Dates Localities Latitude/Longitude Sources
1832-1836 ?? Diego Rarez Islands 5632/6843 Hellmayr & Conover (1949)
Dec.- Feb. 1980-81 Diego Rarez Islands 5632/6843 Schlatter & Riveros (1987)
23 Dec. 1980 Diego Rarez Islands 5632/6843 MZUA
24 Dec. 1980 Diego Ramírez Islands 5632/6843 MZUA
23 Feb. 1989 Islote Gonzalo 5632/6843 Wallace (1991)
18 Dec. 1914 Hornos Island 5554/6717 AMNH
21 Oct. 2002 Hornos Island 5554/6717 Present Study
20 Jan. 2005 Hornos Island 5554/6717 Present Study
11 Jan. 1949 Herschel Island 5551/6720 Orlog (1950)
21 Oct. 2002 Marcial Cove, Herschel Island 5551/6706 Present Study
1832-1836 Ildefonso Island 5550/6917 Hellmayr & Conover (1949)
18 Dec. 1914 Ildefonso Island 5550/6917 AMNH
Dec. 1932 Deceit Island 5550/6707 Reynolds (1935)
26 Mar. 1916 Hermite Island 5550/6740 FMNH
Dec. 1932 Barnevelt Island 5549/6648 Reynolds (1935)
Dec. 1932 Freycinet Island 5547/6713 Reynolds (1935)
16-17 Jan. 1948 Freycinet Island 5547/6713 Orlog (1950)
6-8 Jan. 1948 Baily (=Bayly) Island 5540/6740 Orlog (1950)
20 Feb. 1980 Baily (=Bayly) Island 5540/6740 CZIP
25 Feb. 1980 Lientur Cove, Wollaston Island 5539/6721 CZIP
19 Oct. 2002 Lientur Cove, Wollaston Island 5539/6721 Present Study
3-6 Jan. 1948 Grevy Island 5533/6740 Orlog (1950)
1858 Orange Harbour 5531/6803 Hellmayr & Conover (1949)
22 Dec. 2005 Terhalten Island 5526/6704 Present Study
4 Feb. 2006 Terhalten Island 5526/6704 Present Study
24 Feb. 1968 Nueva Island 5515/6635 Barros (1976)
15 Jan./1 Feb. 1977 Island Hoste 5505/6850 Sielfeld (1977)
4 Feb. 2006 Solitario Island 5459/6708 Present Study
Feb. 1940 Puerto Navarino 5455/6820 Orlog (1948)
Feb. 1940 Yendegaia 5452/6845 Orlog (1948)
11 Feb. 2002 Cockburn / Occasion Channels 5430/7203 Present Study
14-22 Feb. 1984 Noir Island 5429/7302 Clark (1988)
73
DISTRIBUCIÓN DEL CARANCHO NEGRO PHALCOBOENUS AUSTRALIS
Dec. 1983 Noir Island 5429/7302 Venegas (1993)
Nov. 1984 Noir Island 5429/7302 Strange (1996)
11-16 Nov. 2003 Noir Island 5429/7302 Present Study
14-21 Nov. 2004 Noir Island 5429/7302 Present Study
6-19 Nov. 2005 Noir Island 5429/7302 Present Study
29 Jan. 2001 Agostini Sound, “Condor Bay” 5427/7027 Present Study
11 Feb. 2002 Agostini Sound, “Condor Bay” 5427/7027 Present Study
12 Mar. 2001 Agostini Sound, “Condor Bay” 5427/7027 Present Study
19 Mar. 2001 Agostini Sound, “Condor Bay” 5427/7027 Present Study
16 Apr. 2001 Agostini Sound, “Condor Bay” 5427/7027 Present Study
10 Nov. 2003 Dora Island 5416/7228 Present Study
18 Jan. 2006 Tucker Island 5409/7017 Present Study
19 Jan. 2005 Tucker Island 5409/7017 Present Study
15 Feb. 2006 Tucker Island 5409/7017 Present Study
16 Feb. 2001 Tucker Island 5409/7017 Present Study
16 Mar. 2001 Tucker Island 5409/7017 Present Study
15 Apr. 2001 Tucker Island 5409/7017 Present Study
3 Feb. 1984 (Cerro) Helado Sound 5352/7225 Clark, in Strange (1996)
Mar. 1997 Carlos III Island 5340/7220 Present Study
14 Nov. 2005 Leonard Island 5323/7404 Present Study
14 Nov. 2005 Recalada Island 5319/7412 Present Study
15 Nov. 2005 Recalada Island 5319/7412 Present Study
14 Nov. 2005 Inman Island 5318/7417 Present Study
23 Mar. 1979 Recalada Island 5317/7415 CZIP
No date/March (?) Recalada Island 5317/7415 Venegas & Sielfeld (1979)
No date Cabo Pilar 5244/7441 Venegas & Sielfeld (1979)
Mar. 1980 Estancia Consuelo [Puerto Consuelo] 5136/7238 Venegas (1982)
April/March (?) Laguna Amarga 5059/7248 Garay & Guineo (2000)
22 Jan. 1984 Buenaventura Island 5045/7509 Clark in Strange (1996)
No date Guarello Island 5022/7519 Clark et al. (1992)
No date Cabo Primero 4952/7535 Venegas & Sielfeld (1979)
No date Grupo Vorposten 4922/7542 Venegas & Sielfeld (1979)
... The most southerly distributed of all birds of prey, the relatively little-studied Striated Caracara (Phalcoboenus australis) is a medium-sized raptor (approximately 1.5-2.0 kg) with a global, island-restricted breeding range of 30,000 to 46,000 km 2 on the Fuegian regions of Argentina and Chile and outer islands in the Falkland Islands (Islas Malvinas; Ferguson-Lees and Christie 2001, Marín et al. 2006, Birdlife International 2017. Striated Caracaras, which lay up to 4-egg clutches and feed largely on carrion, typically breed in association with seabird colonies (Strange 1996, Woods 2017. ...
... These surveys, which encompassed 54 islands, resulted in an estimated Falklands population of 500 pairs (Woods and Smith 1999). An additional 18 islands surveyed in November 2006 (Woods 2007) suggested that breeding numbers were stable overall, although there were small, local increases on several islands visited in both 1997-1998and 2006-2007(Woods 2007. The surveys suggested that breeding Striated Caracaras are locally numerous on several outer islands in the Falklands, principally the northern and western parts of the archipelago, north and west of the main island of West Falkland, and on outer islands off the southern coast of the main island of East Falkland (Strange 1996, Woods andWoods 1997; Fig. 1) with much smaller numbers nesting on West Falkland itself ( Fig. 1). ...
... The population estimate for 1963-1965 (approximately 40 islands), was 450 pairs, and for subsequent surveys in the 1980s was 337 pairs (approximately 58 islands; Strange 1996). In 1997-1998and 2006, population estimates were 500 and 520 pairs (approximately 54 and 18 islands), respectively Smith 1999, Woods 2007). In addition, an estimated 85 breeding pairs inhabited New Island during the austral summer of 2006-2007(Catry et al. 2008. ...
Article
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We conducted surveys of breeding pairs of the endemic and globally "Near Threatened" Striated Caracara (Phalcoboenus australis) on 79 outer islands in the Falklands archipelago (Islas Malvinas) during the austral-summer breeding seasons of 2013-2014 and 2014-2015. A total of 354 breeding pairs (defined as pairs with evidence of egg-laying), or an archipelago-wide adult breeding population of at least 0.05 birds/km² was recorded. An additional 477 probable breeding pairs also were found. The distribution of breeding pairs remains similar to that found during surveys in the 1990s and 2000s. Grand Jason, Steeple Jason, New Island, Beauchêne Island, and Bird Island, the five islands with the highest numbers of breeding pairs, accounted for half of the total breeding population. "Vegetationally pristine" islands with dense areas of tussac grass (Poa flabellata) and high densities of small burrowing seabirds-namely Bird Island, Saddle Island, and Beauchêne Island-supported the highest densities of breeding pairs. Eighty percent of all pairs occurred on National Nature Reserves or on privately owned nature sanctuaries. Our surveys suggest that sustained protection of key breeding sites is critical for the long-term conservation of this species. We recommend that populations of Striated Caracaras at Tierra del Fuego also be surveyed and that the global population status of the species be reassessed.
... chimango), during the Middle Pleistocene, about 2 Mya (Fuchs, Johnson, and Mindell 2012). The southernmost species, P. australis, diverged roughly 0.6 Mya (Fuchs, Johnson, and Mindell 2012) and present a disjunct distribution restricted to islands in the Fuegian archipelago and the Islas Malvinas/Falkland Islands (IM/FI) (Balza, Lois, and Raya Rey 2017;Balza et al. 2022;Marín et al. 2006;Reeves, Crofts, and Bildstein 2018) (Figure 1). These archipelagos have a markedly different biogeographical history. ...
Article
Aim To understand the influence of Andean uplifts and glacial cycles on South American biodiversity, we delve into the population genetics and evolutionary history of a unique subantarctic island raptor specialised in exploiting marine food webs. Location Islands in Tierra del Fuego and Malvinas/Falklands. Time period Last glacial period to the present. Taxon Phalcoboenus australis . Methods We used RAD sequencing to assess genetic diversity, population structure and to model demographic history through descriptive and hypothesis‐based evolutionary methods. Results We found evidence of two independent lineages: one inhabiting the Fuegian archipelago and the other one occurring in the Islas Malvinas/Falkland Islands, with the latter presenting higher genetic diversity and evidence of finer‐scale population structure. The best supported demographic scenario places the divergence time of these lineages during the last glacial period (ca. 50,000 years ago), with the occurrence of gene flow during the first 27,000 years after their divergence. Recent demographic modelling supports the general pattern of increasing genetic variability as landmasses were uncovered following the glacial period (i.e., the Fuegian archipelago) in contrast with a decrease in genetic diversity associated to island fragmentation (i.e., in the Islas Malvinas/Falkland Islands). Main Conclusions We propose that post‐glacial sea level rise and the subsequent isolation across the submerging Patagonian Shelf have driven population fragmentation and recent genetic structure in this species. Our findings advocate for recognising the two identified divergent lineages as distinct conservation units. We highlight the intricate interplay of ecological factors, glacial cycles and population dynamics in shaping the evolutionary trajectory of this unique and threatened raptor species in southern South America.
... El carancho austral (Phalcoboenus australis, Gmelin 1788), es un caracara endémico de las islas e islotes del extremo sur de la Patagonia y del archipiélago de Malvinas (Strange, 1996;Marín et al., 2006;Birdlife International, 2024). Actualmente está catalogado a nivel global como especie "Cercana a la Amenaza" y a escala nacional como especie En peligro (Aves Argentinas & Ministerio de Ambiente y Desarrollo Sustentable de la Nación, 2017; Birdlife International, 2024). ...
Thesis
Full-text available
Las invasiones biológicas, especialmente en islas, son una causa importante de pérdida de biodiversidad. Aunque su impacto suele ser negativo para la biota nativa, depredadores como las aves rapaces pueden beneficiarse de la incorporación de presas invasoras en su dieta. Para comprender este tipo de interacciones los estudios tróficos son fundamentales, sobre todo antes de realizar acciones de control sobre las invasoras. El carancho austral (Phalcoboenus australis) es una rapaz insular, endémica del sur de Argentina y Chile, que se asocia durante la época reproductiva a colonias de aves marinas. El objetivo de este trabajo fue investigar la ecología trófica del carancho austral en la isla Observatorio durante la época reproductiva, centrándose en el uso de presas introducidas como el conejo de Castilla (Oryctolagus cuniculus) y la rata (Rattus sp.), y comparándolo con el sitio estudiado previamente en bahía Franklin. Mediante análisis de isótopos estables (AIE) de sangre de los pichones y análisis de egagrópilas de los nidos, se caracterizó la dieta de los individuos reproductivos de isla Observatorio y se la comparó con la de los de bahía Franklin. En dos días de trabajo de campo (17 y 18 de diciembre de 2021) se censó a los pares reproductivos en la isla (16 nidos activos). Se tomaron muestras de sangre de 17 pichones de 14 nidos y se recolectaron 102 egagrópilas de 13, junto a muestras de tejido de presas potenciales. Se registró el consumo de especies invasoras en el 69% de los nidos muestreados de isla Observatorio, y el nicho isotópico de los pichones fue hasta más de seis veces mayor que el de los de bahía Franklin, en la que no se detectaron presas introducidas. El principal componente de la dieta en isla Observatorio fue el pingüino magallánico (Spheniscus magellanicus), posiblemente facilitado por la depredación de lobos marinos (Otaria flavescens) sobre los pingüinos, registrada en la bibliografía y en los días de trabajo de campo. El AIE permitió inferir que la mayor amplitud en el nicho isotópico de los pichones de isla Observatorio por sobre los de bahía Franklin estuvo dada por la inclusión de conejo y rata enriquecidos en 15N. La inclusión de invasoras en la dieta de los pichones tiene implicancias en las acciones de manejo a realizar y probablemente también en la dinámica poblacional del carancho austral. El control con rodenticidas debería realizarse con especial cuidado, debido al peligro de envenenamiento secundario de los caranchos, sabiendo que se alimentan de las invasoras. Es posible que el subsidio de las invasoras aumente la densidad de nidos y la supervivencia invernal de la especie en isla Observatorio, por lo que es recomendable que futuros trabajos profundicen en esas líneas.
... The species is known to be present on the island for a long time, as the holotype was collected in 1775 in this site (Strange 1996). Most breeding populations occur in the Malvinas/Falkland archipelago (Reeves et al. 2018), and other breeding sites in the Fuegian archipelago include Franklin Bay (Isla de los Estados), Goffré Island, Noir Island, Diego Ramírez islands and Mitre Peninsula (Tierra del Fuego Main island) (Clark 1984;Parera et al. 1997;Marín et al. 2006;Cursach et al. 2012;Balza et al. 2017). We counted 15 breeding territories and found 10 active nests of Striated Caracara, containing a total of 15 chicks. ...
Article
Full-text available
Continental islands are often sites of low diversity and endemism, as well as important areas for the protection of bird populations, especially seabirds. On Isla Observatorio and the Año Nuevo Islands, in the Southwestern Atlantic, the latest assessment of avifauna dates from more than 20 years ago. In this study, we use a combination of methods to update the status of the main seabird colonies and the most abundant avian terrestrial predator at Observatorio and Goffré Islands during the breeding season. In only 4.5 km², the islands would harbour ~ 90,000 breeding seabirds. Seabird colonies occupied different areas of the islands and varied in their population status, with Imperial Shags (Leucocarbo atriceps) showing an increase and Southern Giant Petrels (Macronectes giganteus) a decrease according to the last surveys. Magellanic Penguin (Spheniscus magellanicus) population estimations also suggest a decrease but the last survey was based on total, and not on occupied nest sites. We recorded and assessed one new breeding species: The globally near-threatened Striated Caracara (Phalcoboenus australis), which has an important breeding population of around 15 territorial pairs at Observatorio Island. These islands appear to be an important regional bird site and future studies would determine their trends and threats, especially those related with invasive species.
... The striated caracara (Phalcoboenus australis, hereafter "caracara") is a near threatened bird of prey restricted to islands in southern South America (BirdLife International, 2018;Frere et al., 1999;Marín et al., 2006;Reeves et al., 2018). During the breeding season, they associate with seabird colonies, breeding in their proximity and feeding on eggs, chicks, adults, and carcasses (Catry et al., 2008;Liljesthröm et al., 2008;Strange, 1996). ...
Article
Full-text available
Optimal foraging theory predicts an inverse relationship between the availability of preferred prey and niche width in animals. Moreover, when individuals within a population have identical prey preferences and preferred prey is scarce, a nested pattern of trophic niche is expected if opportunistic and selective individuals can be identified. Here, we examined intraspecific variation in the trophic niche of a resident population of striated caracara (Phalcoboenus australis) on Isla de los Estados (Staten Island), Argentina, using pellet and stable isotope analyses. While this raptor specializes on seabird prey, we assessed this population's potential to forage on terrestrial prey, especially invasive herbivores as carrion, when seabirds are less accessible. We found that the isotopic niche of this species varies with season, age, breeding status, and, to a lesser extent, year. Our results were in general consistent with classic predictions of the optimal foraging theory, but we also explore other possible explanations for the observed pattern. Isotopic niche was broader for groups identified a priori as opportunistic (i.e., nonbreeding adults during the breeding season and the whole population during the nonbreeding season) than it was for individuals identified a priori as selective. Results suggested that terrestrial input was relatively low, and invasive mammals accounted for no more than 5% of the input. The seasonal pulse of rockhopper penguins likely interacts with caracara's reproductive status by constraining the spatial scale on which individuals forage. Niche expansion in spatially flexible individuals did not reflect an increase in terrestrial prey input; rather, it may be driven by a greater variation in the types of marine prey items consumed.
... En las Islas Malvinas, Isla de los Estados e Islas de Año Nuevo se concentraría al menos el 65% de la población global (BirdLife International 2013). En el continente es raro y si bien se conocen registros para el sur de Chile hasta los 51°S, su reproducción ha sido confirmada en muy pocas localidades, generalmente aisladas entre sí (Meiburg 2006, Marín et al. 2006. En Chile se encuentra al menos presente en el Parque Nacional Cabo de Hornos y las Reservas de las islas Guarello, Noir, Almagro y Diego Ramírez (Chebez 2008). ...
Thesis
Full-text available
Las poblaciones de las mayoría de las aves rapaces son vulnerables y se encuentran amenazadas a nivel global por una serie de características ecológicas comunes: baja productividad y densidades, altos requerimientos de espacio y recursos, vulnerabilidad a compuestos químicos y modificación de su hábitat. El carancho austral (Phalcoboenus australis) es una rapaz endémica del sur de Argentina y Chile, que se encuentra principalmente en islas y normalmente se asocia, durante la época reproductiva, a colonias de aves y mamíferos marinos. El objetivo general de este estudio es aumentar el conocimiento sobre el estado actual de la población y la biología reproductiva del carancho austral en Bahía Franklin, Isla de los Estados, Tierra del Fuego. Se buscaron e identificaron los nidos activos de la especie en el área de estudio durante noviembre y diciembre de 2014. Se realizaron análisis espaciales de patrones de puntos globales, globales ponderados y locales; se modelaron las variables, en relación a su presa principal, que explican la presencia de los nidos; se evaluó el éxito reproductivo y la productividad y se tomaron datos sobre las características de los sitios nido para luego comparar los datos obtenidos con la información disponible en bibliografía. Se encontró un total de 16 nidos activos en el área de estudio, que corresponde con una densidad de 1.43 parejas/km2, el valor más bajo encontrado hasta ahora para la especie. Los nidos se encontraron generalmente de forma agregada.. Las variables que mejor explicaron la presencia de los nidos fueron la cercanía a la colonia de pingüino penacho amarillo (Eudyptes chrysocome) y la visibilidad de la colonia desde el nido. Todos los nidos, excepto dos, estuvieron asociados exclusivamente (en términos de cercanía) con parches de E. chrysocome. El 100% de los nidos accesibles estaban construidos en su mayor parte con fibras de pasto tussock (Poa flabellata) aunque sólo la mitad de los nidos estuvo construida asociada al pastizal de tussock. Para n=11 nidos, el éxito reproductivo aparente fue de 0.73 y la producción total fue de 1.27 ± 1.00 pichones. Existieron diferencias significativas en el éxito reproductivo en función de la distancia al nido de carancho austral más cercano: los nidos que fracasaron en la incubación fueron también los más cercanos entre sí. La dinámica reproductiva de esta especie aparenta ser diferente en el área de estudio a lo que se observa en las Islas Malvinas, donde existen las únicas poblaciones estudiadas de P. australis. Allí, los nidos se disponen de forma regular a la menor distancia posible de la colonia de aves marinas y la mayoría de los nidos están en el suelo. La disposición en núcleos agregados de los nidos, así como observaciones de las características de los sitios de nidificación encontrados, hacen suponer que la densidad reproductiva en esta área está limitada por la escasa disponibilidad de sitios aptos para la construcción del nido. Se propone que la presencia de dos herbívoros introducidos, la cabra (Capra hircus) y el ciervo colorado (Cervus elaphus), están afectando negativamente a la densidad de parejas reproductivas de P. australis, al disminuir la abundancia del pasto tussock y ramonear y pisotear en los alrededores de la colonia de E. chrysocome. Se propone un modelo en el cual además estas especies son un recurso alimenticio importante para P. australis durante el invierno en forma de carroña, ya que en ese momento del año las colonias de aves marinas se encuentran ausentes, y que la reducción en la mortalidad que esto conllevaría, produciría una mayor abundancia total de individuos de P. australis, lo que redundaría en mayor competencia intraespecífica y menor reclutamiento poblacional.
... Striated caracaras are relatively large, stocky, and inquisitive scavenging and predatory birds of prey (Falconiformes). The species breeds in close proximity to seabird colonies, where individuals feed themselves and their developing young on seabird eggs and nestlings, and on dead and dying adult seabirds [12,[15][16][17]. Striated caracaras take marine and terrestrial invertebrates [12] and placentas and carrion of terrestrial livestock and marine mammals [15,18]. ...
Article
Full-text available
Background The extent to which seasonal changes in food availability affect small-scale movements in free-ranging populations of birds of prey is relatively little studied. Here we describe a seasonal “micro-migration” of a farm-island population of striated caracaras (Phalcoboenus australis) in the Falkland Islands in response to seasonal changes in the availability of seabird carcasses. We banded more than 450 individuals on Saunders Island, deployed archival and satellite GPS data loggers on 17 individuals, and monitored movements within and between two feeding areas on Saunders Island, a “marine-subsidized” site near seabird colonies and an anthropogenic “human-subsidized” farm site 16 km to the southeast. Results During 67 observation days between 2010 and 2015, resightings of 312 banded caracaras were greater at the marine-subsidized site during austral summer than winter, and the total daily resightings varied significantly between spring versus summer, summer versus winter, autumn versus spring, and autumn versus winter. Resightings were higher at the human-subsidized site in austral winter than summer and the total daily resightings varied significantly across all bi-seasonal comparisons. Resightings indicated that at least 12 of 197 birds (6.1%) moved between the human- and marine-subsidized sites at least once during the same winter, 15 of 335 birds (4.5%) did so in spring, none of 164 birds did so in summer, and 16 of 297 birds (5.4%) did so in autumn. Individuals fitted with archival GPS data loggers at the marine-subsidized site in summer maintained highly localized 95% kernel core areas (0.55 ± 0.12 km² [mean ± SD]), whereas those at the human-subsidized site in winter maintained larger 95% kernel core areas (3.8 ± 4.6 km²). Two of 6 satellite-tagged individuals that summered at known caracara breeding colonies 80 km WNW of Saunders Island were subsequently resighted in winter at the human-subsidized site. Conclusion Our results suggest that seasonal shifts in food resource availability drive seasonal micro-migrations in a farm-island population of striated caracaras, and that farm sites can be critical in providing nutritional resources for caracaras when naturally occurring marine-subsidized resources become less available. Our results have important implications for striated caracara spatial ecology and conservation, as increased winter survival could improve the status of this globally Near-Threatened population.
... Striated caracaras are relatively large, stocky, and inquisitive scavenging and predatory birds of prey (Falconiformes). The species breeds in close proximity to seabird colonies, where individuals feed themselves and their developing young on seabird eggs and nestlings, and on dead and dying adult seabirds [12,[15][16][17]. Striated caracaras take marine and terrestrial invertebrates [12] and placentas and carrion of terrestrial livestock and marine mammals [15,18]. ...
... The species is classified as Near Threatened (IUCN 2015) with an extant population of ,2,500 mature individuals. They reside mostly on Staten Island (Isla de los Estados) in the Fuegian region and in the Malvinas/Falkland Islands (BirdLife International 2013), with fragmented breeding records in southern Chile (Marín et al. 2006). The species is largely associated with seabird breeding colonies (i.e., Rockhopper Penguins [Eudyptes chrysocome], Black-browed Albatross [Thalassarche melanophris]). ...
Article
Full-text available
The Striated Caracara (Phalcoboenus australis) is a poorly known raptor associated with seabird colonies, restricted to the islands of southern South America, and with an estimated extant population of <2,500 mature individuals. We evaluated the number of breeding pairs, described the characteristics and spatial pattern of nest sites, and estimated breeding output of a population of Striated Caracaras in Franklin Bay, Staten Island, Argentina. We found one of the lower breeding density values reported for this species, although this population is associated with one of the biggest colonies of Rockhopper Penguins. The main material used for the construction of Striated Caracaras' nests was tussac grass, though only half of nests were placed in grassland. The spatial pattern for nest sites corresponds with global and local clustering. All successful Striated Caracaras' nests were at least 250 m from the nearest neighboring nest, were generally closer to the colony of Rockhopper Penguins than failed nests, and had more Rockhopper patches around them. Breeding success was 0.73 successful nests/active nests, productivity was 1.27 ± 1.01 young/active nest, and brood size was 1.75 ± 0.71 young/successful nest. The presence of invasive wild goats and red deer is proposed as a factor that could be restricting nest site availability in the study area.
Article
Breeding outcome in birds can be influenced by both intrinsic and extrinsic factors, and these may contribute differentially to each stage of the breeding cycle. Island raptors are relatively threatened species that rely on simplified food webs and usually co-occur with invasive species. Here, we studied a population of Striated Caracara (Phalcoboenus australis) in Isla de los Estados (Argentina) to understand the relative contribution of food availability, topographic features and territoriality to breeding parameters. Caracaras in the area depend on the short seasonal (i.e., pulsed) availability of seabirds for feeding their chicks. On the other hand, the recent introduction of non-native ungulates may have led to a suboptimal breeding environment by reducing caracara nest site availability within the seabird colonies via disturbance of the grassland. Using data from seven breeding seasons we analyse the abundance, the proportion of breeding individuals, the spatial structure of breeding events and the population-level breeding performance, including chick sex-ratio, to study whether the breeding ecology of this species is still shaped by marine food web pulses or if it could be associated with invasive herbivore disturbance. The breeding adults in the population represented only 6-15% of the population. The spatial pattern of nest sites did not differ from random arrangement after considering the heterogeneous distribution of food availability. Territory identity accounted for most of the variation in clutch size and productivity, while penguin availability explained part of the variability in territory occupancy and hatching rate. The chick sex ratio was biased towards females and varied according to brood size, with the more productive territories producing 91% of males. The breeding cycle of this population is still mainly dependent upon the Rockhopper Penguin food pulse and presents mixed evidence of being disrupted by invasive herbivores. The studied factors contributed differentially to the output of each reproductive stage, with territory identity accounting for most of the variation. Our results suggest that individual-level, long term data could be relevant to understanding the dynamics of this species in the Fuegian archipelago, and thus a broad-scale research program is warranted to assess the conservation status and propose future management scenarios for this species.
Article
Full-text available
Fifteen raptor species (Falconiformes and Strigiformes) breed and other two may breed in Torres del Paine National Park (Chilean Patagonia), the highest raptor species richness documented in Chile. Accounts for each raptor species in Torres del Paine are provided, including information on weight, habitat, diet, residence, conservation, and miscellaneous observations in the Park. We compare raptor species richness in Torres del Paine with well studied localities in central and northern Chile, and speculate on causes for the higher raptor diversity observed in the Park. Raptor macroniches in Torres del Paine are assessed, describing primarily their use of two major habitat types and nine food resources. We examine food-niche relationships for a subset of four mammal-eating raptors, in light of their different ecologies and body sizes. A monitoring program for raptors in Torres del Paine is proposed, under the rationale that these indicator species may help foresee impending disruptions of basic ecosystem processes that determine the relatively pristine conditions still prevailing in the Park.