Ibis (2009), 151, 514–522
Gyrfalcon Falco rusticolus post-glacial colonization
and extreme long-term use of nest-sites in Greenland
KURT K. BURNHAM, 1,2 * † WILLIAM A. BURNHAM 2‡ & IAN NEWTON 3
Department of Zoology, Edward Grey Institute, University of Oxford, South Parks Road, Oxford OX1 3PS, UK
2
The Peregrine Fund, 5668 West Flying Hawk Lane, Boise, ID 83709, USA
3
Centre for Ecology & Hydrology, Maclean Building, Benson Lane, Crowmarsh Gifford, Wallingford, Oxon OX10 8BB, UK
1
Gyrfalcons Falco rusticolus use the same nest-sites over long periods of time, and in the
cold dry climate of Greenland, guano and other nest debris decay slowly. Nineteen guano
samples and three feathers were collected from 13 Gyrfalcon nests with stratified faecal
accumulation in central-west and northwest Greenland. Samples were 14C dated, with
the oldest guano sample dating to c. 2740–2360 calendar years (cal yr) before present
(BP) and three others were probably > 1000 cal yr BP. Feather samples ranged from 670
to 60 cal yr BP. Although the estimated age of material was correlated with sample
depth, both sample depth and guano thickness gave a much less reliable prediction of
sample age than use of radiocarbon dating on which the margin of error was less. Older
samples were obtained from sites farther from the current Greenland Ice Sheet and at
higher elevations, while younger samples were closer to the current ice sheet and at
lower elevations. Values for d13C showed that Gyrfalcons nesting farther from the
Greenland Ice Sheet had a more marine diet, whereas those nesting closer to the ice
sheet (= further inland) fed on a more terrestrial diet. The duration of nest-site use by
Gyrfalcons is a probable indicator of both the time at which colonization occurred and
the palaeoenvironmental conditions and patterns of glacial retreat. Nowhere before has
such extreme long-term to present use of raptor nest-sites been documented.
Keywords: carbon dating, guano, palaeoenvironmental conditions, d13C.
It is well known that raptors may re-use nest-sites
for generations and some possibly for centuries
(Newton 1979). Hickey (1942) referred to these
nest-sites as ‘ecological magnets’. These locations
are evidently so desirable that they are re-used
again and again, even if the birds have no former
familiarity with the location. For example, Peregrine Falcons Falco peregrinus disappeared from
large areas of North America and Europe during
the 1960s as a result of organochlorine pesticide
use. Many years later, following the restriction in
the use of these chemicals, released or recolonizing
Peregrines usually reoccupied former territories
*Corresponding author.
Email: kburnham@higharctic.org
†
Present address: High Arctic Institute, 603 10th Avenue,
Orion, IL 61273, USA.
‡
Deceased.
ª 2009 The Authors
Journal compilation ª 2009 British Ornithologists’ Union
first, frequently re-using the same nest ledges their
predecessors did (Newton 1979, Ratcliffe 1993,
Oakleaf 2003).
Gyrfalcons Falco rusticolus and Peregrine Falcons
both breed in the Arctic. Falcons do not build
nests, but lay eggs in bowl-shaped depressions they
scrape into existing substrates, including old nests
made by other birds. Arctic Peregrine Falcons typically use open ledges on cliffs for nesting with little
protection from the weather (Cade 1960). Gyrfalcons usually nest on cliff ledges overhung by rock,
in potholes, or in sheltered stick-nests built by
Northern Ravens Corvus corax (Cade 1960,
Burnham & Mattox 1984). These nesting situations
provide protection from falling rock and the
extreme weather conditions often found during
the early part of the Gyrfalcon breeding season.
While stick nests are frequently damaged beyond
re-use in a single season, some ledges and potholes
Gyrfalcon long-term nest use
are used long-term by Gyrfalcons (Burnham &
Mattox 1984). Gyrfalcons and Northern Ravens do
not seem to alternate the use of the same nest-site
from year to year in Greenland. At re-used sites,
faecal accumulation frequently occurs where Gyrfalcons roost and nest. Deposited over periods of
years, the stratified accumulation of guano can
become greater than 1.5 m thick in locations protected from erosion and where dry and cold environmental
conditions
enhance
preservation
(Fig. 1). There are many such nest-sites throughout ice-free areas of Greenland.
The Greenland Ice Sheet covers 82% of the land
mass of Greenland (Ohmura et al. 1999), and icefree land occurs only along the periphery of the
island. Nest-site availability for falcons may be
affected by climate-induced glacial retreat and
advance covering and exposing cliffs. Long-term
use of nest-sites by Gyrfalcons is a potential indicator for palaeoenvironments and of stable glacial
conditions. As the ice sheet retreated, areas at
higher elevations, having a thinner layer of ice and
snow, were exposed first. Land at lower elevations,
particularly valley bottoms, had the thickest covering of ice and was exposed last (Fristrup 1966).
We therefore hypothesized that guano in Gyrfalcon nests at lower elevations and closer to the current ice sheet would have accumulated over
shorter periods than that at nests at higher elevations and further from the current Greenland Ice
Sheet. To investigate this question we sampled and
radiocarbon dated guano from Gyrfalcon nest-sites
in two areas, in Kangerlussuaq, central-west
515
(66.50–67.00 N), and Thule, northwest (76.25–
77.17 N), Greenland. These study areas were separated by about 9 latitude and 1100 km.
Study areas
The Kangerlussuaq study area is located at the
head of a 175-km-long fjord and about 25 km
from the current ice sheet margin. The Low Arctic
tundra landscape in this area was sculpted by glaciation, with rolling hills and valleys, moraines and
lakes, dissected by several meltwater rivers, and
dominated mainly by shrubs up to 2 m in height.
Primary prey species for Gyrfalcons in Kangerlussuaq include both Rock Ptarmigan Lagopus mutus
and Arctic Hare Lepus arcticus, with lesser quantities of passerines and waterfowl consumed (Booms
& Fuller 2003). It is one of the largest deglaciated
land areas in Greenland and, because of extensive
past research, provides one of the most complete
records of Greenland’s glacial history (Ten Brink &
Weidick 1974, Eisner et al. 1995). From projected
rates of deglaciation (see below), we can estimate
that some Gyrfalcon nest-sites may have been
uncovered c. 6500–6000 years before the present
(yr BP).
The Thule study area is centred around Pituffik ⁄ Thule Air Base and the current ice sheet margin lies up to 26 km inland from the sea, but it
reaches the sea at several locations. The environment is High Arctic with an appearance of recent
deglaciation, and sparsely vegetated prostrate
growing herbs and shrubs. In this area, Gyrfalcons
fed primarily on Little Auks Alle alle, Rock Ptarmigans and Arctic Hares, with seabirds, waterfowl,
and passerines taken in smaller numbers (Burnham
2008). Information on glaciation in Thule is more
limited than for Kangerlussuaq, and glacial history
is predicted more from inference of past climates
than from moraine locations and measurement
(Davies et al. 1963, Fredskild 1985, Kelly et al.
1999). Deglaciation sufficient to allow for consistent use of existing Gyrfalcon nest-sites may not
have occurred until 1350 yr BP or more recently
(see below).
METHODS
Figure 1. Gyrfalcon nest-site 123 being sampled for radiocarbon dating in Kangerlussuaq, central-west Greenland, with a
14
C age of 1160–920 cal yr BP.
Gyrfalcon nest-sites are distributed widely and
irregularly throughout the two study areas and
ice-free Greenland as a whole. All sites are on
cliffs and usually inaccessible without technical
ª 2009 The Authors
Journal compilation ª 2009 British Ornithologists’ Union
516
K. K. Burnham et al.
rock-climbing equipment. The amount of faecal
material build-up at sites varies greatly, as does the
structure and size of the nest. The rock substrate
upon which falcon guano accumulates is usually
irregular, sloping, and seldom flat. Particularly on
large ledges, the actual nest scrape is not always in
the same exact location each year, nor is the associated faecal deposition resulting from breeding.
Also, the rates of erosion are probably not constant
across the nest, as some locations in the nest are
more protected from weather than are others.
Therefore, the guano is not of constant depth
throughout the site, and it is difficult to know
where the thickest and ⁄ or oldest deposits may lie.
At nest-sites where deposits seemed of more-orless uniform thickness throughout, a single sample
was collected where guano came in contact with
the rock, while at other sites more than one sample was collected in an attempt to obtain the oldest
guano. Bulk sample materials were collected from
several centimetres of stratified guano, probably
representing accumulation over decades or longer.
Notes were made of sample depth (cm), cliff
height (m), and nest ledge elevation (meters above
sea level, m asl). All nests sampled had been occupied by Gyrfalcons within the past 25 years
(Table 1).
When collecting samples, layers of faecal buildup were excavated carefully to prevent damage of
the site for future use by Gyrfalcons. At nest-sites
with only a few centimetres of faecal build-up, we
dug vertically down into the guano, extracted
samples at its base, and then refilled the hole to
minimize damage to the nest-site. At sites with
substantial build-up, samples were taken from the
side by using a masonry hammer and a small
trowel to excavate horizontally until rock was
reached. The amount of bulk material collected
from the stratified samples varied, but in all cases
was sufficient for dating using standardized
radiocarbon procedures. Within the nest-sites,
feathers (from probable prey and ⁄ or Gyrfalcons)
and bones (prey) were found during excavation.
Three feathers that were easily identifiable as from
Gyrfalcons were also radiocarbon dated.
Radiocarbon dating was carried out by Beta Analytic Inc., Miami, FL, USA, using either the conventional radiometric technique (samples > 30 g) or
accelerator mass spectrometry (AMS) (samples < 30 g). Guano samples were pre-treated using
an ‘acid wash’, and an ‘acid ⁄ alkali ⁄ acid’ wash was
used for feather samples. For the conventional
ª 2009 The Authors
Journal compilation ª 2009 British Ornithologists’ Union
radiometric technique, materials were analyzed by
synthesizing carbon to benzene (92% C) and then
measuring for 14C in a scintillation spectrometer
from which the radiocarbon age was calculated
(Beta Analytic Inc. 2005). AMS results were
obtained by the reduction of sample carbon to
graphite (100% C) along with standards and backgrounds (Beta Analytic Inc. 2005). Graphite was
then sent for 14C measurement in an acceleratormass-spectrometer to a research facility collaborating with Beta Analytic. The measured radiocarbon
ages were returned to Beta Analytic where verification, isotopic fractionation correction using d13C,
and calendar calibration took place (Beta Analytic
Inc. 2005). Calibrated results provide both a maximum and minimum age for each sample in calendar
years (cal yr) before present (BP), with a 95% confidence that the actual age falls within this range.
Calibrations were made using calibration data published in Stuiver et al. (1998) using cubic spline fit
mathematics, as described by Talma and Vogel
(1993).
From 2002 to 2004, 19 bulk guano samples and
three feathers were collected from 13 Gyrfalcon
nest-sites. Five guano samples and one feather
were from four nests in Thule, and 14 guano samples and two feathers from nine nests in Kangerlussuaq. To test for relationships between age of
guano samples and nest variables (using JMP IN, v. 4,
SAS Institute Inc., Cary, NC, USA), we analyzed
the distribution of the variables and relationships
using Spearman correlation analysis, as was most
appropriate based on the non-normal distribution
of the data. Conventional 14C age was used as the
maximum age for each sample.
RESULTS
The oldest guano sample was from nest-site 087 in
Kangerlussuaq and was dated 2740–2360 cal yr BP
(Table 1). Three nests in Kangerlussuaq showed
evidence of occupation > 1000 cal yr BP, with the
most recent nest being first occupied from 650 to
520 cal yr BP. In Thule, the oldest nest was between
690 and 530 cal yr BP, with two nests indicating use
only within the past 50 years (Table 1). Sites in
Kangerlussuaq seem to have been used approximately 1800–2000 years longer than those further
north in Thule. Sites with multiple samples
collected showed an increase in 14C age with sample
depth (Table 1). The three analyzed Gyrfalcon
feathers were between 670 and 60 cal yr BP. Sample
Gyrfalcon long-term nest use
517
Table 1. Results of the 14C measurements on guano material and feathers from Gyrfalcon nest-sites in Kangerlussuaq, central west,
and Thule, northwest Greenland, collected from 2002 to 2004. Samples from the same nest-site are designated by the use of A, B, C,
or D following the number. No specific nest locations are given in order to protect against possible collection of eggs and chicks.
Nest-site
Beta
Analytic
sample #
Sample
depth
(cm)
Cliff
height
(m)
Kangerlussuaq, central-west Greenland
019
195586
20–25
15
053A
191125
30–35
15
053B
191126
15–20
15
Conventional
14
C age
(yr BP ± 1r)
Nest
elevation
(m asl)
Distance
from ice
margin (km)
d13C
(&) (PDB)c
355
304
304
9
11
11
)22.7
)22.4
)22.4
1992
1991
1991
790 ± 60
1290 ± 50
1090 ± 80
320 ± 30
570 ± 50
240 ± 60
Last
used
053Ca
068A
068B
191295
191127
195576
15
15–20
10–15
15
152
152
304
55
55
11
14
14
)22.5
)22.9
)20.7
1991
2000
2000
082
087A
087B
087C
195577
168839
168840
168838
25–30
30–35
25–30
0–3
76
46
46
46
441
365
365
365
5
54
54
54
)23.2
)21.9
)20.9
)24.2
1999
2002
2002
2002
087Da
168837
15
46
365
54
)21.3
2002
123
163
170
201A
195578
195587
195579
195580
46
152
24
23
258
395
103
200
62
72
28
78
)21.1
)20.8
)21.3
)17.8
1985
2003
2004
2000
23
200
78
)21.3
2000
46
152
14
)23.3
2003
113.34 ± 0.71 pMCb
20–25
100–110
15–20
35–40
201B
195581
10–15
Thule, northwest Greenland
500A
195583
5–8
830
2480
350
105.09
±
±
±
±
70
40
40
0.66 pMCb
170 ± 40
1090
960
690
1430
±
±
±
±
60
60
60
70
820 ± 60
500B
195582
3–6
46
152
14
)21.2
2003
122.08 ± 0.73 pMCb
501
195584
2–4
117
122
2
)23.2
2004
115.29 ± 0.66 pMCb
502
503A
503Ba
195585
191124
191348
15–20
20–25
20
23
76
76
152
304
304
9
17
17
)20.2
)19.1
)19.5
2004
2004
2004
640 ± 50
650 ± 70
650 ± 40
Calibrated age
range
(cal yr BP ± 2r)
790–650
1300–1080
1180–900,
850–810
470–300
650–520
450–260,
220–140,
30–0
920–660
2740–2360
500–300
outside
calibration
rangeb
300–60,
40–0
1160–920
970–740
710–550
1480–1470,
1430–1250
910–660
outside
calibration
rangeb
outside
calibration
rangeb
outside
calibration
rangeb
670–540
690–530
670–550
a
Gyrfalcon feather samples.
pMC (percent Modern Carbon) analyzed material was post-1950 and had more 14C than did the AD 1950 reference standard due to
atomic bomb testing and subsequent fall-out; 50 years was used as conventional 14C age, while Calibrated Age Range is outside calibration range.
c
PD belemnite.
b
087D had two possible calibrated age ranges, 300–
60 and 40–0 cal yr BP, and the older range was most
likely accurate based on other samples from the
same nest and sample depth. While the bulk samples
of guano represent a number of years of site use, the
feathers were from a precise moment in time.
The maximum conventional 14C age for each
individual nest was significantly correlated with the
current distance from the ice margin (rs = 0.56,
P < 0.05, n = 13; Fig. 2), nest elevation (rs = 0.61,
P < 0.05, n = 13; Fig. 3), and sample depth
(rs = 0.88, P < 0.0001, n = 13; Fig. 4). While
sample depth could be used as a predictor of 14C
age, the margin of error would be much greater
than if using radiocarbon dating directly (e.g. 087A
& 163, Fig. 4).
ª 2009 The Authors
Journal compilation ª 2009 British Ornithologists’ Union
Distance from ice margin (km)
518
K. K. Burnham et al.
sample from each nest varied slightly from a median of )21.9& (n = 9, r2 = 2.7) for Kangerlussuaq
to )21.5& (n = 4, r2 = 4.5) for Thule, with no
statistical difference between the two areas. A
significant correlation exists between d13C for the
oldest guano sample from each nest and current
distance to the Greenland Ice Sheet (rs = 0.63,
P < 0.05, n = 13), with less negative values being
associated with nests farther from the current ice
sheet (Fig. 5).
90
80
201a
163
70
123
60
087a
50
40
30
170
20
504a
500a 068a
10
0
0
053a
019
503
082
502
500
1000
1500
2000
2500
3000
Conventional c-14 age (years BP)
Nest elevation (m)
Figure 2. Relationship between maximum
site distance from current ice margin.
500
450
400
350
300
250
200
150
100
50
0
14
DISCUSSION
C age and nest-
082
163
087a
019
053a
503a
123
201a
500a
502
501
170
068a
0
500
1000
1500
2000
2500
3000
Conventional c-14 age (years BP)
Figure 3. Relationship between maximum
site elevation (m above sea level).
14
C age and nest-
Sample depth (cm)
120
163
100
80
60
40
503a
20
068a
500a
501
0
0
502
500
082
019
123
170
1000
201a
087a
053a
1500
2000
2500
3000
Conventional c-14 age (year BP)
Figure 4. Relationship between maximum
sample depth.
14
C age and
In general, organisms from marine food chains
or animals that feed on them have less negative
d13C values, while more negative d13C values are
typically associated with terrestrial ecosystems
(Rounick & Winterbourn 1986, Angerbjörn et al.
1994). The d13C values from the oldest guano
ª 2009 The Authors
Journal compilation ª 2009 British Ornithologists’ Union
Radiocarbon dating of Gyrfalcon nest material
from Kangerlussuaq and Thule, Greenland, indicate much longer occupancy times than can be
determined from historical records. Sites from
Kangerlussuaq were colonized approximately
1800–2000 years earlier than those further north
in Thule, probably an effect of earlier deglaciation
and a more stable and warmer climate in the Kangerlussuaq area. These are some of the longest
used raptor nest-sites ever documented.
Similar studies of this type have been carried
out on other Arctic and Antarctic species. These
have included Snow Petrels Pagodroma nivea
(Hiller et al. 1988), Thick-billed Murres Uria
lomvia (Gaston & Donaldson 1995), and Adelie
Penguins Pygoscelis adeliae (Emslie et al. 2007), for
which radiocarbon age has been calculated using
solidified stomach oil deposits, peat moss deposits,
and bone and feather samples from moulting sites,
respectively, and minimum dates for the establishment or colonization of bird colonies have been
given ( 34 000 yr BP, 1500–3800 yr BP, and
> 44 000 yr BP, respectively). In addition, archaeological studies have sometimes revealed long-term
use of raptor nest-sites. For example, remains of
Peregrine Falcons, probably adults and nestlings,
were found during an archaeological investigation
of prehistoric human occupation of a cave on
Hunter Island, Tasmania (Bowdler 1984). Bones
were found in layers 990 ± 90 to c. 19 000 yr BP,
suggesting use by falcons during that time but not
more recently.
There can be little doubt about the identity of
the Gyrfalcon sites in Greenland. Only two falcon
species breed there (Salomonsen 1950) and,
although Peregrines sometimes use former
Gyrfalcon nest-sites, these species typically select
different nesting situations, as explained above.
Cliff-nesting seabirds breed in different situations
201A 80
80
60
60
40
40
20
20
163
123
087A
170
Snowshoe
Hare
(-26.4)
Rock
Ptarmigan
(-24.4)
500A
068A
082
501
–24
503
053A
–23
502
019
Little
Auk
Black
Guillemo t
0
–17
0
–22
–21
–20
–19
–18
519
Distance from ice marging (km)
Gyrfalcon long-term nest use
δ13C ‰
Figure 5. Relationship between d13C and distance from current ice margin. Frequent prey of Gyrfalcons shown with associated d13C
value. d13C values for Snowshoe Hare Lepus americanus (substituted for Arctic Hare as no values were found in the literature for Arctic Hare), Rock Ptarmigan, Little Auk, and Black Guillemot are from Roth et al. (2007), Ricca et al. (2007), and Hobson et al. (2002).
than do falcons. Gulls nest colonially and sites
cannot be confused with falcon nests. Except for
Iceland Gulls Larus glaucoides and Glaucous Gulls
Larus hyperboreus, all other avian species breeding
in the research areas construct nests containing
sticks, grass, and feathers, and ⁄ or breed on the
ground. Ravens are the only other cliff-nesting
species that nest in similar locations to Gyrfalcons,
but they construct stick-nests. There can be no
doubt that the accumulation of guano at sites
sampled resulted from long-term use by falcons,
and in particular Gyrfalcons.
The feather samples could be easily identified to
Gyrfalcons. Although interesting because of their
condition and long-term preservation, they did not
contribute to knowledge on duration of nest-site
use or palaeoenvironment beyond what could be
inferred from guano samples. They did, however,
provide confirmation of dates of past use.
Some nest-sites provided much older radiocarbon-dated samples than others. Newton (1979)
attributed the repeated occupancy of nest-sites to
‘the superiority of particular places over local alternatives’. This superiority could result from a
nearby abundance of prey, a superior hunting platform, a location in appropriate spatial relationship
to other territorial pairs, or a site offering good protection from mammalian predators or inclement
weather (rain, snow, sun, and ⁄ or wind). Over time,
the desirability of sites may change due to altered
environmental conditions, including rock structure.
This likelihood may be particularly true in areas of
recent glacial activity and climate change.
The Greenland ice sheet gradually retreated
about 175 km in the Kangerlussuaq area because
of world-wide climate warming since the end of
the last glaciation ( 15 000 yr BP), but with fre-
quent re-expansions (Ten Brink & Weidick 1974,
Funder 1989) (Fig. 6). A slow retreat of the ice
sheet (1 km ⁄ 100 years) occurred from c. 15 000 to
10 000 yr BP followed by an oscillatory but more
rapid retreat (3 km ⁄ 100 years) of nearly 100 km
from c. 9500 to 6500 yr BP (Ten Brink & Weidick
1974). By 6000 yr BP the ice sheet had reached its
present position, although between 5- and 10-km
re-advances occurred from c. 4800 to 4000 and
from 2500 to 2000 yr BP (Ten Brink & Weidick
1974) (Fig. 6). At that time the sea level was
nearly at that of the present day. Eisner et al.
(1995) reported that Kangerlussuaq experienced a
‘climatic optimum’ from c. 4400 to 3400 yr BP
and that a climatically stable period is believed to
have also encompassed the period from 2000 to
1200 yr BP (Fig. 6). Based on lichenometry, the
period from c. 700 yr BP to the present was characterized by oscillatory advance and retreat of the
inland ice within about a 3-km-wide zone (Ten
Brink & Weidick 1974).
In Kangerlussuaq, nest-sites 019, 053, 068, 082,
and 170 were probably covered by ice during
re-advances of glaciers from the Greenland ice
sheet between c. 4800 and 4000 and from 2500 to
2000 yr BP. All five nest-sites are in glacial valleys
or river valleys and four of the five are on low
cliffs. The fifth site (053) is near the top edge of a
deep valley. Furthermore, 068 and 170 are on
small cliffs near low elevation rivers and even a
10-m rise in sea level could have affected use of
these sites by Gyrfalcons. Nest-sites 087, 123, 163,
and 201 are < 50 km from the ice edge and, based
on the projected rate of ice sheet retreat, these
nest-sites were ice-free by 6500–6000 yr BP. That
does not preclude, however, the possibility of isolated snow banks and glaciers covering nest-sites,
ª 2009 The Authors
Journal compilation ª 2009 British Ornithologists’ Union
520
K. K. Burnham et al.
Kangerlussuaq
Thule
0 year BP
Oscillatory advance/retreat
First Gyrfalcon nest
1
Warming period
2
Cooling period
Stable climate
Minor ice re-advance
First Gyrfalcon nest
3
Climatic optimum
?
Minor ice re-advance
4
5000
Ice sheet at current position
Holocene climatic optimum
6
7
Rapid ice retreat
8
?
9
10 000
11
Wolstenholme Fjord glaciation
Slow ice retreat
12
13
14
15 000 year BP
Figure 6. Glacial and climate history for the past 15 000 yr BP for the Kangerlussuaq and Thule study areas. For sources on dates
used in the figure please see text.
particularly on small cliffs and at lower elevations,
during periods of climatic cooling and glacial
expansion. In addition, it was probably not until
the ‘climatic optimum’, from 4400 to 3400 yr BP,
that the necessary vegetation was established to
support the prey-base utilized by Gyrfalcons in
Kangerlussuaq.
Information from Thule is far less complete and
more contentious than that from Kangerlussuaq. In
Thule, Malaurie et al. (1972) used data from
marine deposits of terraces to estimate that deglaciation began c. 8000 yr BP, and Kelly et al. (1999)
postulate that much of the area has been ice-free
for at least 9000 years (Fig. 6). From the period
extending 8000–3000 yr BP the Thule area experienced a climatic optimum, with significant surface
melting occurring (Reeh 1984) (Fig. 6). Archaeological evidence indicates unfavourable, cool condi-
ª 2009 The Authors
Journal compilation ª 2009 British Ornithologists’ Union
tions from 2500 to 1900 yr BP followed by three
centuries with a warmer climate (McGhee 1972)
(Fig. 6). During the period c. 1350–900 yr BP a
moist and probably warm climate prevailed, with
conditions cooling and vegetation changing to drier
heath at the end of this period (Fredskild 1973)
(Fig. 6). From c. 900 yr BP to the 20th century,
considerable climatic variability existed, but evidence from ice cores and oxygen isotopic records
from Camp Century show that generally cooler
conditions probably persisted in the Thule area
until c. 1900 AD (Johnsen et al. 1970). Meteorological records from Upernavik, Greenland (7250¢N),
show a 2C mean annual temperature increase
through the middle of the 20th century (Dowdeswell 1996).
In Thule, the existence of consistent longterm nest-site availability is more recent than in
Gyrfalcon long-term nest use
Kangerlussuaq. While some nest-sites may have
been ice-free as early as c. 9000–6000 yr BP, they
may have been later re-covered by re-advances of
the ice sheet. Furthermore, despite some nest-sites
being ice-free for extended periods of time, suitable environmental conditions for Gyrfalcons probably did not exist until between 1350 and 900 yr
BP or later. Even now, because of cool mean summer temperatures, localized large snow banks and
glaciers can develop in just a few years or decades
and preclude the use of affected nest-sites.
The significant correlation between d13C values
and distance to the current ice sheet is probably a
reflection of diet, with Gyrfalcons breeding nearer
the coast feeding on a mixed diet of marine and
terrestrial prey items, and those breeding more
inland having an almost completely terrestrial diet.
Primary terrestrial prey items, such as Rock Ptarmigan and Arctic Hare, have probable d13C values
in the range of )24 to )27& (Fig. 5) (Ricca et al.
2007, Roth et al. 2007), while marine prey items,
such as Little Auks and Black Guillemots Cepphus
grylle, have d13C values ranging from )18 to )20&
(Fig. 5) (Hobson et al. 2002). Other prey species
taken in more limited quantities, such as shorebirds (e.g. Red Knot Calidris canutus and Ruddy
Turnstone Arenaria interpres) and waterfowl (e.g.
Long-tailed Duck Clangula hyemalis), have d13C
values with much wider ranges ()16.6 to )24.7&,
)18.1 to )24.1&, )17 to )21&, respectively),
mainly as a result of seasonal shifts in foraging
between marine and terrestrial areas (Morrison &
Hobson 2004, Braune et al. 2005).
In Kangerlussuaq, d13C values for each of the oldest 14C dated nests ranged from )23.2 to )17.8&.
Nest 082 has the most negative d13C value and is
closest to the current ice sheet (5 km), and nest
201A has the least negative d13C value and is
farthest from the ice sheet (78 km) (Fig 5). Of
particular interest is nest 087A, which is the oldest
sampled nest in Kangerlussuaq by 1000 years, and
has the median d13C of the nine nests sampled in
Kangerlussuaq. Although this nest is 54 km from
the current ice sheet, it is approximately 1 km from
a large fjord, allowing adult Gyrfalcons potential
access to both a marine and terrestrial diet. The benefit of readily accessing such a large variety of prey
may have allowed for earlier colonization of the
nest-site. For Thule, nests 500A and 501 have very
negative d13C values, with nest 500A almost
100 km from the nearest breeding seabird colonies
and prey remains consisting almost solely of Arctic
521
Hare in recent years, and nest 501 in a large wetland
area, with prey remains primarily consisting of Rock
Ptarmigan. The other two Thule nest-sites, 502 and
503A, are in areas with large numbers of Little Auks
and Black Guillemots. For both study areas multiple
samples from the same nest-site show changes of up
to )3& in d13C over time (e.g. site 087 in Kangerlussuaq, Table 1), which is probably the result of
changes in prey composition over time.
On the basis of palaeoenvironmental investigations by others, we hypothesized that Gyrfalcon
nest-sites of higher elevations, and further from
the ice margin, would show longer usage patterns
than nest-sites closer to the ice edge, and at lower
elevations. Both predictions were confirmed using
14
C dating. Carbon dating of stratified guano accumulation at Gyrfalcon nest-sites could thus be
used to confirm and date when local environments
were suitable for breeding by this species and
when colonization probably occurred. Furthermore, past use of sites indicates that favourable
environmental conditions existed for prey species
as well. Values from d13C provide insight into
likely prey species that existed at the time of colonization and possible changes in prey species over
time. While results from this study are specific to
Kangerlussuaq and Thule, it is possible that similar
correlations exist in other regions of Greenland.
These results shed further light on local, and probably regional, palaeoenvironmental conditions and
glaciation in the Arctic.
First and foremost we thank Andrew Gosler, Jennifer
Burnham, Jeff Johnson, Chris Perrins, and David Houston for comments and suggestions. Additionally, Konrad
Steffen, University of Colorado, USA, provided helpful
remarks on this manuscript and suggested citations
related to glaciation and palaeoenvironments in Greenland. Edward Hanna, University of Plymouth, UK,
provided further citations related to glaciation and
palaeoenvironments in Greenland. Thank you to the
Greenland Home Rule Government and Danish Polar
Center for providing permits for this research. Additionally, the support of KISS, VECO, 109th Air National
Guard, and the United States Air Force were critical in
supporting field work. Brian and Ruth Mutch, Jack
Cafferty, Jack Stephens, Robin Abbott, Earl Vaughn, Ed
Stockard, and the residents of both Kangerlussuaq and
Thule Air Base deserve special thanks for their continued
friendship and assistance. Financial support was provided
by The Peregrine Fund, Ruth O. Mutch, The Offield
Family Foundation, Peter Pfendler, Comer Science
and Education Foundation, and The G. Unger Vetlesen
Foundation and is greatly appreciated.
ª 2009 The Authors
Journal compilation ª 2009 British Ornithologists’ Union
522
K. K. Burnham et al.
REFERENCES
Angerbjörn, A., Hersteinsson, P., Lidén, K. & Nelson, E.
1994. Dietary variation in arctic foxes (Alopex lagopus) – an
analysis of stable carbon isotopes. Oecologia 99: 226–232.
Beta Analytic Inc. 2005. 4985 S. W. Court, Miami, FL, 33155,
USA. http://www.radiocarbon.com.
Booms, T. & Fuller, M. 2003. Gyrfalcon diet in central west
Greenland during the nesting period. Condor 105: 528–537.
Bowdler, S. 1984. Hunter Hill, Hunter Island: Archaeological
Investigation of a Prehistoric Tasmanian site. Terra Australis 8. Canberra: Australian National University Press.
Braune, B.M., Hobson, K.A. & Malone, B.J. 2005. Regional
differences in collagen stable isotope and tissue trace element profiles in populations of long-tailed duck breeding in
the Canadian Arctic. Sci. Total Environ. 346: 156–168.
Burnham, K.K. 2008. Inter- and Intraspecific Variation of
Breeding Biology, Movements, and Genotype in Peregrine
Falcon Falco peregrinus and Gyrfalcon F. rusticolus Populations in Greenland. D.Phil. Thesis, University of Oxford.
Burnham, W.A. & Mattox, W.G. 1984. Biology of the Peregrine and Gyrfalcon in Greenland. Meddelelser om Grønland: Bioscience 14: 1–25.
Cade, T.J. 1960. Ecology of the Peregrine and Gyrfalcon
populations in Alaska. Univ. Calif. Publ. Zool. 63: 151–290.
Davies, W.E., Krinsley, D.B. & Nicol, A.H. 1963. Geology of
North Star Bay area, northwest Greenland. Meddelelser om
Grønland 162: 1–68.
Dowdeswell, J.A. 1995. Glaciers in the High Arctic and recent
environmental change. Philos. Trans. R. Soc. Lond.: Phys.
Sci. Eng. 352: 321–334.
Eisner, W.R., Tornqvist, T.E., Koster, E.A., Bennike, O. &
van Leeuwen, J.F.N. 1995. Paleoecological studies of a
Holocene lacustrine record from the Kangerlussuaq
(Søndre Strømfjord) region of West Greenland. Quatern.
Res. 43: 55–66.
Emslie, S.D., Coats, L. & Licht, K. 2007. A 45,000 yr old
record of Adélie penguins and climate change in the Ross
Sea, Antarctica. Geology 35: 61–64.
Fredskild, B. 1973. Studies in the vegetational history of
Greenland. Meddelelser om Grønland 198: 1–245.
Fredskild, B. 1985. The Holocene vegetational development
of Tugtuligssuaq and Qeqertat, northwest Greenland. Meddelelser om Grønland, Geoscience 14: 1–20.
Fristrup, B. 1966. The Greenland Ice Cap. Copenhagen:
Rhodos, International Science Publishers.
Funder, S. 1989. Quaternary geology of the ice-free areas and
adjacent shelves of Greenland. In Fulton, R.J. (ed.) Quaternary Geology of Canada and Greenland: 741–792. Ottawa:
Geological Society of Canada.
Gaston, A.J. & Donaldson, G. 1995. Peat deposits and
Thick-billed Murre colonies in Hudson Strait and Northern
Hudson Bay: clue to post-glacial colonization of the area by
seabirds. Arctic 48: 354–358.
Hickey, J.J. 1942. Eastern population of the Duck Hawk.
Auk 59: 176–204.
Hiller, A., Wand, U., Kämpf, H. & Stackebrandt, W. 1988.
Occupation of the Antarctic continent by petrels during the
past 35,000 years: inferences from a 14C study of stomach
oil deposits. Polar Biol. 9: 69–77.
Hobson, K.A., Gilchrist, G. & Falk, K. 2002. Isotopic investigations of seabirds of the north water polynya: contrasting
ª 2009 The Authors
Journal compilation ª 2009 British Ornithologists’ Union
trophic relationships between the eastern and western
sectors. Condor 104: 1–11.
Johnsen, S.J., Dansgaard, W., Clausen, H.B. & Langway,
C.C. 1970. Climatic oscillations 1200–2000 AD. Nature 227:
482–483.
Kelly, M.S., Funder, M., Houmark-Nielsen, K.L., Knudsen,
K.L., Kronbory, C., Landvik, J. & Sorby, L. 1999. Quaternary glacial and marine environmental history of northwest
Greenland: a review and reappraisal. Quatern. Sci. Rev.
18: 373–392.
Malaurie, J., Vasari, Y., Hyvarinen, H., Delibrias, G. &
Labeyrie, J. 1972. Preliminary remarks on Holocene paleoclimates in the regions of Thule and Inglefield Land, above
all since the beginning of our own era. Acta Univ. Oul. A 3.
Geol. 1: 105–133.
McGhee, R. 1972. Climatic change and the development of
Canadian Arctic cultural traditions. Acta Univ. Oul. A 3.
Geol. 1: 39–57.
Morrison, R.I.G. & Hobson, K.A. 2004. Use of body stores in
shorebirds after arrival on High-Arctic breeding grounds.
Auk 121: 333–334.
Newton, I. 1979. Population Ecology of Raptors. Berkhamsted:
T. & A.D. Poyser.
Oakleaf, R. 2003. Peregrine restoration from a state biologist’s
perspective. In Cade, T.J. & Burnham, W. (eds) Return
of the Peregrine, a North American Saga of Tenacity
and Teamwork: 297–304. Boise, ID: The Peregrine Fund.
Ohmura, A., Calanca, P., Wild, M. & Anklin, M. 1999. Precipitation, accumulation and mass balance of the Greenland
Ice Sheet. Z. Gletsherk. Glazialgeol. 35: 1–20.
Ratcliffe, D. 1993. The Peregrine Falcon. London: T & AD
Poyser.
Reeh, N. 1984. Reconstruction of the glacial ice covers of
Greenland and the Canadian Arctic islands by three-dimensional, perfectly plastic ice-sheet modeling. Ann. Glaciol.
5: 115–121.
Ricca, M.A., Miles, A.K., Anthony, R.G., Deng, X. & Hung,
S.S.O. 2007. Effect of lipid extraction on analysis of stable
carbon and stable nitrogen isotopes in coastal organisms of
the Aleutian archipelago. Can. J. Zool. 85: 40–48.
Roth, J.D., Marshall, J.D., Murray, D.L., Nickerson, D.M. &
Steury, T.D. 2007. Geographical gradients in diet affect
population dynamics of Canada Lynx. Ecology 88: 2736–
2743.
Rounick, J.S. & Winterbourn, M.J. 1986. Stable carbon isotopes and carbon flow in ecosystems. Bioscience 36: 171–
177.
Salomonsen, F. 1950. Grønlands Fugle ⁄ Birds of Greenland.
Copenhagen: Ejnar Munksgaard.
Stuiver, M., Reimer, P.J., Bard, E., Beck, J.W., Burr, G.S.,
Hughen, K.A., Kromer, B., McCormac, G., van der
Plicht, J. & Spurk, M. 1998. INTCAL98 Radiocarbon Age
Calibration. Radiocarbon 40: 1041–1083.
Talma, A.S. & Vogel, J.C. 1993. A simplified approach to
calibrating C14 Dates. Radiocarbon 35: 317–322.
Ten Brink, N.W. & Weidick, A. 1974. Greenland Ice Sheet
history since the last glaciation. Quatern. Res. 4: 429–440.
Received 10 March 2009;
accepted 27 April 2009.