ArticlePDF Available

Arctic sea ice a major determinant in Mandt's black guillemot movement and distribution during non-breeding season

Authors:
  • Cooper Island Arctic Research

Abstract and Figures

Mandt's black guillemot (Cepphus grylle mandtii) is one of the few seabirds associated in all seasons with Arctic sea ice, a habitat that is changing rapidly. Recent decreases in summer ice have reduced breeding success and colony size of this species in Arctic Alaska. Little is known about the species' movements and distribution during the nine month non-breeding period (September–May), when changes in sea ice extent and composition are also occurring and predicted to continue. To examine bird movements and the seasonal role of sea ice to non-breeding Mandt's black guillemots, we deployed and recovered (n = 45) geolocators on individuals at a breeding colony in Arctic Alaska during 2011–2015. Black guillemots moved north to the marginal ice zone (MIZ) in the Beaufort and Chukchi seas immediately after breeding, moved south to the Bering Sea during freeze-up in December, and wintered in the Bering Sea January–April. Most birds occupied the MIZ in regions averaging 30–60% sea ice concentration, with little seasonal variation. Birds regularly roosted on ice in all seasons averaging 5 h d−1, primarily at night. By using the MIZ, with its roosting opportunities and associated prey, black guillemots can remain in the Arctic during winter when littoral waters are completely covered by ice.
Content may be subject to copyright.
rsbl.royalsocietypublishing.org
Research
Cite this article: Divoky GJ, Douglas DC,
Stenhouse IJ. 2016 Arctic sea ice a major
determinant in Mandt’s black guillemot
movement and distribution during
non-breeding season. Biol. Lett. 12: 20160275.
http://dx.doi.org/10.1098/rsbl.2016.0275
Received: 4 April 2016
Accepted: 17 August 2016
Subject Areas:
ecology
Keywords:
seabird, Arctic, sea ice, black guillemot,
geolocation
Author for correspondence:
G. J. Divoky
e-mail: divoky@cooperisland.org
One contribution to the special feature ‘Effects
of sea ice on Arctic biota’.
Electronic supplementary material is available
online at https://dx.doi.org/10.6084/m9.fig-
share.c.3457497.
Marine biology
Arctic sea ice a major determinant in
Mandt’s black guillemot movement and
distribution during non-breeding season
G. J. Divoky1, D. C. Douglas2and I. J. Stenhouse3
1
Friends of Cooper Island, 652 32nd Avenue E, Seattle, WA 98112, USA
2
US Geological Survey Alaska Science Center, 250 Egan Drive, Juneau, AK, USA
3
Biodiversity Research Institute, 276 Canco Road, Portland, ME 04103, USA
GJD, 0000-0001-9902-8203; DCD, 0000-0003-0186-1104; IJS, 0000-0003-3614-9862
Mandt’s black guillemot (Cepphus grylle mandtii) is one of the few seabirds
associated in all seasons with Arctic sea ice, a habitat that is changing
rapidly. Recent decreases in summer ice have reduced breeding success
and colony size of this species in Arctic Alaska. Little is known about the
species’ movements and distribution during the nine month non-breeding
period (SeptemberMay), when changes in sea ice extent and composition
are also occurring and predicted to continue. To examine bird movements
and the seasonal role of sea ice to non-breeding Mandt’s black guillemots,
we deployed and recovered (n¼45) geolocators on individuals at a breeding
colony in Arctic Alaska during 20112015. Black guillemots moved north to
the marginal ice zone (MIZ) in the Beaufort and Chukchi seas immediately
after breeding, moved south to the Bering Sea during freeze-up in December,
and wintered in the Bering Sea January– April. Most birds occupied the MIZ
in regions averaging 30– 60% sea ice concentration, with little seasonal
variation. Birds regularly roosted on ice in all seasons averaging 5 h d
21
, pri-
marily at night. By using the MIZ, with its roosting opportunities and
associated prey, black guillemots can remain in the Arctic during winter
when littoral waters are completely covered by ice.
1. Introduction
While the Arctic supports a large and diverse marine avifauna in summer, most
seabirds migrate south in autumn as several million square kilometres of sea ice
growth reduces the amount of ocean available for foraging in winter. Only two
seabird species have their migrations and winter distributions determined by the
formation and presence of Arctic sea ice, the high Arctic populations of black
guillemot (Cepphus grylle) and the ivory gull (Pagophila eburnea) [1]. Black guille-
mots in the western Arctic are in the subspecies mandtii [2], thought to have
occupied a high Arctic refugium in the last glacial maximum [3] with geographi-
cal variation in the mitochondrial DNA of our study population on Cooper
Island reinforcing that view [4]. Black guillemots are pursuit diving piscivores
that in the Beaufort and Chukchi seas prey heavily on Arctic cod (Boreogadus
saida) [57], the primary fish species associated with Arctic sea ice [8]. Black guil-
lemots have been observed in the Alaskan Arctic at the ice edge during autumn
[6], and as far north as Pt. Barrow [9] and as far south as the ice edge in the Bering
Sea [10] during winter, but nothing has been documented about non-breeding
habitat use, movements and regional distributions.
Arctic sea ice has been decreasing significantly in recent decades with com-
plete loss in summer possible for mid-century [11], so it is important to
document use of sea ice by one of the few Arctic avian ‘sea ice obligates’. To
this end, we deployed light-sensitive geolocators and data loggers on breeding
&2016 The Author(s) Published by the Royal Society. All rights reserved.
on September 8, 2016http://rsbl.royalsocietypublishing.org/Downloaded from
black guillemots at the Cooper Island colony to extend our
knowledge of the subspecies during the non-breeding period.
2. Material and methods
Geolocators were deployed and retrieved at Cooper Island,
Alaska (718200N, 1558410W, figure 1). Breeding black guillemots
were fitted with 1 g geolocators near the end of four breeding
seasons, 20112014, and retrieved the following year. We used
British Antarctic Survey (Cambridge, UK) units (Mk13 or Mk14)
in 20112012 and Migrate Technology (Cambridge, UK) units
(C-65) in 20132014. We attached the geolocator to a plastic leg
band on the bird’s tarsus with a cable tie. The number of geoloca-
tors deployed annually were 6, 9, 26 and 18; with 5, 7, 23 and 10
retrievals, respectively.
We derived noon and midnight positions based on sunset and
sunrise times estimated from light intensity levels that were
sampled every 60 s with maximums stored every 5 min. We
used INTIPROC software (Migrate Technology) to estimate latitude,
based on day length and longitude, based on time of midday
with respect to GMT. Black guillemots sometimes roosted on sea
ice near the time of sunrise and sunset, obscuring the light
sensor and preventing reasonable position estimates. We excluded
estimates before 16 October and between 1 March and 15 April,
because latitudes are unreliable around the vernal and autumnal
equinoxes, and after 1 May, because birds were moving northward
into areas with near 24 h of daylight. After exclusions, we used
1334, 1855, 4993 and 2564 position estimates for analysis of the
four non-breeding periods, respectively.
We used the kernelkcbase function in the R library adehabi-
tatHR [12] with a 150 km smoothing parameter to generate
twice-monthly utilization distributions (UDs) on a fixed 50 km
resolution grid. Twice-monthly UDs were computed with all
years pooled, and for individual years. We used the pooled
UDs to map generalized movements, and the year-specific UDs
to calculate average sea ice concentration [13] within 50% UD
contours during the period of occupancy and +one month.
We used wet/dry logs from Migrate Technology geolocators to
investigate time spent out of water, diurnally and seasonally. Black
guillemots in the western Arctic are regularly seen roosting on sea
ice (G. Divoky 2016, personal observation), and we believe dry
state to be primarily indicative of roosting although an unknown
portion of thedry hours may be of a bird tucking its tarsus and geo-
locator into its plumagewhile in the water, as has been observed for
other alcids [14]. Loggers interrogated wet/drystate every 30 s and
stored cumulative wet-counts every 4 h. We assumed wet/drystate
reflected a 30 s period and computed time dry for each 4 h logging
period. To examine diurnal variation in time dry, we used mid-time
of each 4 h logging period to bin data into four 6 h diurnal periods,
starting at 03.00, 09.00, 15.00, 21.00 local time (GMT-10 h). We also
partitioned data at monthly scales to examine seasonal variations:
post-breeding in the Beaufort and Chukchi seas during Septem-
ber– November, movements to the Bering Sea during December,
winter in the Bering Sea during January–March, and initial
spring migration during April.
3. Results
(a) Distribution and movements
Black guillemots fitted with geolocators completed breeding
between 22 August and 5 September. Although no reliable
geolocator locations were obtained until 16 October, sea sur-
face temperature (SST) and wet/dry state in early September
indicated birds moved north to the sea ice after departing the
breeding colony. The Cooper Island black guillemots
undergo a full-body moult immediately after breeding,
usually completed by late September off northern Alaska
[6], with movements prevented or impaired during flight
feather replacement. Post-breeding movements were primar-
ily northward with the majority of black guillemots between
728and 758N in late October with some individuals possibly
as far north as 778N.
Westward movement into the Chukchi Sea did not occur
until late November as ice covered the Beaufort Sea. Most
birds moved into the Bering Sea from late November to late
December as the Chukchi Sea became ice-covered. From
Figure 1. Pooled locations (dots) of adult Mandt’s black guillemots (n¼45) in twice-monthly periods during four non-breeding seasons (20112015) with
average sea ice concentration during the same periods. Polygons depict 90% (thin) and 50% (thick) utilization distributions. Birds were tagged with geolocators
at their Cooper Island breeding colony near Barrow, Alaska.
rsbl.royalsocietypublishing.org Biol. Lett. 12: 20160275
2
on September 8, 2016http://rsbl.royalsocietypublishing.org/Downloaded from
January through to April, black guillemots broadly occupied
the partially ice-covered Bering Sea shelf, although a few
individuals returned to the Arctic Basin in February in
some years. Most birds remained in the Bering Sea through
late April, when sea ice was rapidly melting and retreating.
A directed migration northward out of the Bering Sea
occurred in late April and early May when large numbers
of black guillemots begin to stage in open water leads off
Pt. Barrow before returning to Cooper Island in early June
(C. George 2015, personal communication.).
(b) Ice habitat
Black guillemots occupied sea ice habitat in the marginal ice
zone (MIZ) during the entire non-breeding period (figure 2).
While sea ice was forming during October to late February,
birds consistently occupied broad areas where the mean ice
concentration was 43% (s.d. 9.8), averaging 20% more than
a month earlier and 20% less than a month later. In April,
with sea ice melting and retreating, this pattern reversed
and birds continued to occupy regions with similar ice con-
centrations by moving north into areas that earlier had had
more ice. SST data loggers in the 2013 and 2014 deployments
showed birds moved from relatively warm waters (more than
38C) near the colony to waters averaging less than 18C (i.e.
near sea ice) for the remainder of the non-breeding period.
(c) Behaviour
Black guillemots averaged over 5 h per day out of water
throughout the non-breeding period (table 1). Most time
out of water involved night-time roosting on sea ice, with
an average of 3.8 h dry from 21.00 to 09.00 (GMT-10 h), and
less than 1 h from 09.00 to 15.00. Seasonal variation was
low with the exception of January– March in the Bering Sea
when birds spent almost 1.5 h more out of the water than
the other three seasonal periods.
4. Discussion
Our study provides, to our knowledge, the first detailed infor-
mation on movements and habitat use of one of the Northern
Hemisphere’s most northerly wintering seabirds and a truly
pagophilic population adapted to occupyArctic sea ice habitats
p
eriod
100
80
60
40
20
0
late
Oct Nov Dec Jan Feb Apr
lateearly late late lateearly early early late
ice concentration (%)
Beaufort
Chukchi Chukchi Chukchi
Bering Bering
occupancy
one month pre-occupancy
one month post-occupancy
Figure 2. Average sea ice concentration (+1 s.d.) within annual (n¼4 years) twice-monthly 50% utilization distributions (UDs) of Mandt’s black guillemots
(blue), and within the same UDs one month before (green) and one month after (red) occupancy.
Table 1. Mean hours per day Mandt’s black guillemots spend out of water, diurnally and seasonally, during the non-breeding period.
03.0009.00 09.00 15.00 15.00 21.00 21.0003.00
hours dryperiod location mean s.d. mean s.d. mean s.d. mean s.d.
SepNov Beaufort/Chukchi 1.35 1.56 0.55 0.68 1.37 1.51 1.72 1.86 4.99
Dec Chukchi/Bering 1.72 2.01 0.52 0.69 1.05 1.48 1.73 2.04 5.02
JanMar Bering 2.38 2.18 0.47 0.65 1.04 1.35 2.58 2.38 6.47
Apr Bering 1.28 1.56 0.74 0.90 1.32 1.46 1.79 1.88 5.14
SepApr 1.78 1.94 0.54 0.71 1.20 1.45 2.05 2.13 5.14
rsbl.royalsocietypublishing.org Biol. Lett. 12: 20160275
3
on September 8, 2016http://rsbl.royalsocietypublishing.org/Downloaded from
throughout the year. Most members of the genus Cepphus inha-
bit near shore littoral waters in breeding and non-breeding
seasons [15], where they use a prey base that is more predict-
able, less patchy and at shallower depths, while maintaining
access to coastal roosting sites. In regions where the littoral
zone is ice-covered for much of the year, pelagic sea ice offers
a proxy to coastal habitat by providing sympagic fauna and a
roosting substrate. Mandt’s black guillemot probably became
adapted to sea ice habitats when restricted to an unglaciated but
ice-covered refugium in the Arctic during the last glacial maxi-
mum [4], and the observations presented here demonstrate a
continued association with that habitat.
The physical and biological changes associated with sea
ice formation and melt are the primary factors influencing
black guillemot movements in the western Arctic. Migration
in the non-breeding period was primarily facultative, being
correlated with the advancement of sea ice. Interannual move-
ments responded to short-term variations (i.e. +two weeks) in
sea ice distribution that were averaged in figure 1. While unpre-
dictable annual and seasonal variation in prey availability is
the primary stimulus for most facultative movements in birds
[16], the southward movements appeared not to be limited
solely to prey but in response to the southward shift of the
MIZ. Movement related to suitable sea ice habitat and not
necessarily prey has been recorded in Antarctic seabirds [17].
It is not known if Arctic cod also move with the advancing
ice. Black guillemots prey on Arctic cod at the advancing ice
edge in autumn [6,18], and the size and depth of Arctic cod
in the Bering are suitable for black guillemots [19]. While
Arctic cod or alternative prey may be most available at the
ice concentrations favoured by black guillemots in the MIZ,
benefits offered by physical ice characteristics may play an
important role in habitat preferences. Because black guillemots
spend approximately 20% of the day roosting on sea ice, birds
may be selecting areas with appropriate ice thickness and con-
centration for roosting. The benefits of roosting versus sitting
on the water are negatively correlated with water tempera-
ture, so ice suitable for roosting would be essential when
occupying the freezing winter waters of the Bering Sea, as it
is for spectacled eiders (Somateria fischeri) wintering there [20].
Conditions south of preferred ice may be less optimal for
roosting, foraging and protection from storms owing to an
abundance of thin frazil ice in low concentrations or compe-
tition from seabird species less adapted to sea ice. The
observed departure from areas of increasing ice concentration
could be in response to decreased foraging opportunities in
heavy ice, or to increased risks of occupying areas where
open water could rapidly disappear from wind-driven compac-
tion or sudden freezing, which is known to be a source of
mortality for wintering black guillemots [21]. While most indi-
viduals occupied the MIZ, it is important to note that once ice
formation was nearly complete in February, birds broadly occu-
pied much of the Bering/Chukchi shelf with some positioned
southerly, whereas others had returned to the Arctic Basin.
Recent losses in summer sea ice have impacted black
guillemot breeding success on Cooper Island, owing to
diminished accessibility to Arctic cod, but annual adult survi-
val has shown no trend over the past four decades [7]
indicating no decadal trend in prey availability in the MIZ.
Future changes in Arctic sea ice can be expected to cause
major alterations in the distribution and timing of Mandt’s
black guillemot movements and distribution as summer ice
is predicted to disappear and winter ice to greatly decrease
in this century [22,23].
Ethics. Animal handling protocols were approved by US Geological
Survey (bird banding permit no. 21675).
Data accessibility. Location and wet/dry sensor data are available in the
electronic supplementary material.
Authors’ contributions. G.J.D. conceived the study assisted by I.J.S. G.J.D.
conducted the fieldwork. G.J.D. and D.C.D. performed analyses. All
authors wrote the manuscript, approved the final version, and agree
to be held accountable for the manuscript’s contents.
Competing interests. We have no competing interests.
Funding. Support for fieldwork and analyses (G.J.D.) were provided by
the non-profit organization Friends of Cooper Island.
Acknowledgements. We thank the Biodiversity Research Institute for pro-
viding geolocators in 2011 to initiate the study, the North Slope
Borough’s Department of Wildlife Management for logistical support
of fieldwork on Cooper Island, and Penelope Chilton for assisting
with fieldwork and data processing. Any use of trade, firm, or pro-
duct names is for descriptive purposes only and does not imply
endorsement by the US Government.
References
1. Spencer NC, Gilchrist HG, Mallory ML. 2014 Annual
movement patterns of endangered ivory gulls: the
importance of sea ice. PLoS ONE 9, 19. (doi:10.
1371/journal.pone.0115231)
2. Gabrielson IN, Lincoln FC. 1959 The birds of Alaska,
922 pp. Harrisburg, PA: Stackpole Co.
3. Salomonsen F. 1972 Zoogeographical and ecological
problems in arctic birds. Proc. Int. Ornithol. Congr.
15, 2577.
4. Kidd MG, Friesen VL. 1998 Analysis of mechanisms
of microevolutionary change in Cepphus guillemots
using patterns of control region variation. Evolution
52, 11581168. (doi:10.2307/2411245).
5. Eckert CG. 2014 Black guillemot population and nest
success at Herschel IslandQikiqtaruk Territorial
Park, Yukon. Report on the 2014 nesting season.
Whitehorse, Canada: Yukon Parks.
6. Watson GE, Divoky GJ. 1972 Pelagic bird and
mammal observations in the eastern Chukchi Sea,
early fall 1970. In WEBSEC-70. An ecological survey
in the eastern Chukchi Sea, SeptemberOctober
1970. pp. 111172. U.S. Coast Guard. Oceanogr.
Report 50.
7. Divoky GJ, Lukacs PM, Druckenmiller ML. 2015
Effects of recent decreases in arctic sea ice on an
ice-associated marine bird. Prog. Oceanogr. 136,
151161. (doi:10.1016/j.pocean.2015.05.010)
8. Lonne OJ, Gulliksen B. 1991 Source, density and
composition of sympagic fauna in the Barents Sea.
Polar Res. 10, 289– 294. (doi:10.1111/j.1751-8369.
1991.tb00654.x)
9. Bailey AM. 1948 Birds of arctic Alaska. Popular
Series No. 8, 317 pp. Denver, CO: Colorado Museum
of Natural History.
10. Kessel B, Gibson DD. 1978 Status and distribution of
Alaska birds. Stud. Avian. Biol..1, 1– 100.
11. Wang M, Overland JE. 2012 A sea ice free summer
Arctic within 30 years: an update from CMIP5
models. Geophys. Res. Lett. 39, L18501. (doi:10.
1029/2012GL052868)
12. Calenge C. 2006 The package ‘adehabitat’ for the R
software: a tool for the analysis of space and
habitat use by animals. Ecol. Model. 197, 516 519.
(doi:10.1016/j.ecolmodel.2006.03.017)
13. Cavalieri DJ, Parkinson CL, Gloersen P, Zwally HJ.
1996 (updated yearly) Sea Ice Concentrations from
Nimbus-7 SMMR and DMSP SSM/I-SSMIS Passive
Microwave Data, Version 1. National Snow and Ice
Data Center, Boulder, CO, USA.
14. Harris MP, Daunt F, Bogdanova MI, Lahoz-Monfort JJ,
Newell MA, Phillips RA, Wanless S. 2013 Inter-year
rsbl.royalsocietypublishing.org Biol. Lett. 12: 20160275
4
on September 8, 2016http://rsbl.royalsocietypublishing.org/Downloaded from
differences in survival of Atlantic puffins Fratercula arctica
are not associated with winter distribution. Mar. Biol.
160, 28772889. (doi:10.1007/s00227-013-2278-5)
15. Gaston AJ. 2004 Seabirds: a natural history.New
Haven, CT: Yale University Press.
16. Newton I. 2012 Obligate and facultative migration
in birds: ecological aspects. J. Ornithol.153,
S171S180. (doi:10.1007/s10336-011-0765-3)
17. Ainley DG, Ribic CA, Spear LB. 1993 Species-habitat
relationships among Antarctic seabirds: a function of
physical and biological factors. Condor.95,
806816. (doi:10.2307/1369419)
18. Divoky GJ. 1984 The pelagic and nearshore birds of
the Alaskan Beaufort Sea: biomass and trophics. In
The Alaskan Beaufort Sea: ecosystems and
environments (eds PW Barnes, DM Schell, E Reimnitz),
pp. 417–437. New York, NY: Academic Press.
19. Lowry LF, Frost KJ. 1981 Distribution. growth, and
foods of Arctic cod (Boreogadus saida) in the Bering,
Chukchi and Beaufort seas. Can. Field-Nat. 95,
186191.
20. Lovvorn JR, Grebmeier JM, Cooper LW, Bump JK,
Richman SE. 2009 Modeling marine protected areas
for threatened eiders in a climatically changing
Bering Sea. Ecol. Appl.19, 15961613. (doi:10.
1890/08-1193.1)
21. Bianchi VV, Karpovitsch VN. 1969 The influence of
abnormal ice cover of the White Sea and Murman in
1966 upon birds and mammals. Zool. Z. 48, 871–875.
22. Overland JE, Wang MY. 2013 When will the summer
Arctic be nearly sea ice free? Geophys. Res. Lett. 40,
20972101. (doi:10.1002/grl.50316)
23. Wang MY, Overland JE. 2015 Projected future
duration of the sea-ice-free season in the Alaskan
Arctic. Progr. Oceanogr. 136, 50– 59. (doi:10.1016/j.
pocean.2015.01.001)
rsbl.royalsocietypublishing.org Biol. Lett. 12: 20160275
5
on September 8, 2016http://rsbl.royalsocietypublishing.org/Downloaded from
... The species is a single-prey loader that raises up to two chicks (Cairns 1987b;Divoky et al. 2021). In the Arctic, the species is often associated with sea ice (Divoky et al. 2016). In sub-arctic and temperate seas, however, black guillemots stay within the coastal zone (here including the continental shelf) and usually within 100 km of the nearest land all year-round and typically undertake rather short migrations (< 500 km) during the non-breeding season (Ewins 1988;Ewins and Kirk 1988;Bakken et al. 2003;Baak et al. 2021). ...
... It thus seems very likely that black guillemots are able to forage under nautical twilight conditions, especially since the species also winters along the coastline of North Norway and along the ice edge in Svalbard, as well as in other high-Arctic environments (e.g. Divoky et al. 2016). Daylength during winter is short at these latitudes, and other diving seabirds wintering in the Arctic are also known to forage during civil and nautical twilight conditions (e.g. ...
Article
Full-text available
The intensification of coastal development poses potential threats for coastal seabirds, and understanding their habitat use is a key factor to guide conservation and management. In sub-arctic areas, black guillemots (Cepphus grylle) use coastal habitats year-round, which makes them vulnerable to the increasing human activities in these areas. In mainland Norway, one of the species’ strongholds, black guillemots are red-listed after substantial population declines. However, their fine-scale foraging behaviour has received little attention to date. We collected and analysed GPS tracking data from adult black guillemots at three sites located over a latitudinal gradient of 250 km in central/northern Norway. Maximum foraging ranges of 33 km at Sklinna (65°12′N) for incubating birds, and 18 km at both Vega (65°34′N) and Sklinna for chick-rearing birds, are among the longest reported for this species. At all three sites, foraging probability was highest in shallow waters (< 50 m depth) close to the colony and declined with increasing water depth and distance from colony. However, birds from Vega also foraged over deeper waters. Kelp presence was of high importance at Sklinna, but apparently less important at Røst (67°26’N) and Vega. We also found distinct differences in foraging activity across the day and with tidal height among the sites. Inter-site differences in habitat use and foraging activity may be explained by differences in the availability of habitats and suitable prey. Our study highlights the importance of shallow marine areas for black guillemots and shows that habitat use can vary substantially between sites.
... For foraging animals, aggregations are likely where food is abundant and available (Fretwell & Lucas 1970;Stephens et al. 2007). Seabirds are known to aggregate in the Arctic marginal ice zone because of the good feeding conditions (Bradstreet 1979(Bradstreet , 1980Lønne & Gabrielsen 1992;Divoky et al. 2016), with similar patterns in the Antarctic (e.g., Tarroux et al. 2020). Arctic seabirds, particularly surface feeders, also aggregate near tidewater glaciers (also known as marine-terminating glaciers) in the melting season (McLaren & Renaud 1982;Lydersen et al. 2014;Stempniewicz et al. 2017;Nishizawa et al. 2020;Bertrand et al. 2021). ...
... It eats small fish and larger zooplankton, as well as benthic organisms (Lydersen et al. 1989;Lønne & Gabrielsen 1992;Divoky et al. 2021). The black guillemot can also be common offshore at seaice edges (Bradstreet 1979;Divoky et al. 2016). When found in glacial bays, black guillemots are less closely associated with glacier fronts than surface-feeding species, such as the black-legged kittiwake (Rissa tridactyla; Lydersen et al. 2014;Stempniewicz et al. 2017). ...
Article
Full-text available
Seabirds in cold biomes sometimes aggregate near glacier fronts and at sea-ice edges to forage. In this note, we report on large aggregations of black guillemots (Cepphus grylle) at the edge of sea ice in front of the tidewater glacier Kongsbreen (Kongsfjorden, Svalbard). During several days in the second half of June 2011, we observed 49–155 individuals of black guillemots at this ice edge. They foraged actively, and many of the dives were directed underneath the sea ice. The outflow of glacial meltwater and resulting upwelling generated opportunities for the black guillemots to feed, likely on zooplankton or fish. The black guillemots used the sea ice as a resting platform between dives or diving sessions, and whilst on the ice, they interacted socially. On our last visit, the sea ice was gone, and the black guillemots had left the bay. At the neighbouring tidewater glacier Kronebreen, there was no sea ice connected to the glacier. Surface-feeding seabirds, particularly black-legged kittiwakes (Rissa tridactyla), were numerous at the plumes generated by meltwater from Kronebreen. Black guillemots were not seen at these plumes, but some individuals were seen scattered in the fjord system. Our observations add to the natural history of black guillemots and enhance our knowledge of ecological interactions and seabird habitat use shaped by tidewater glaciers.
... For example, lack of under-ice algae, a preferred food of copepods, can lead to reduced populations of Arctic cod and consequently top predators that prefer cod (Gaston et al., 2005;Yurkowski et al., 2017Yurkowski et al., , 2018. Indeed, reductions in accessible, sympagic Arctic cod are a common theme across the Arctic with reductions in Arctic cod in the diet of many marine predators; the cod may still be there but may be difficult to detect if they are not associated with readily visible ice (Gaston et al., 2005;Gaston and Elliott, 2014;Divoky et al., 2015Divoky et al., , 2016. The match-mismatch hypothesis is a classic mechanism for bottom-up regulation associated with climate change (Thomas et al., 2001). ...
... Thus, although the timing of ice-off has advanced by over a month in Hudson Bay, Canada, the timing of the breeding of seabirds has only advanced by a few days. Consequently, seabirds are nourishing their offspring after Arctic cod, their preferred prey, is no longer accessible, leading to smaller chicks (Gaston et al., 2005;Gaston and Elliott, 2014;Divoky et al., 2015Divoky et al., , 2016Fig. 2). ...
Article
Global climate change has led to profound alterations of the Arctic environment and ecosystems, with potential secondary effects on mercury (Hg) within Arctic biota. This review presents the current scientific evidence for impacts of direct physical climate change and indirect ecosystem change on Hg exposure and accumulation in Arctic terrestrial, freshwater, and marine organisms. As the marine environment is elevated in Hg compared to the terrestrial environment, terrestrial herbivores that exploit coastal/marine foods when terrestrial plants are iced over may be exposed to higher Hg concentrations. However, certain populations of predators, including Arctic fox and polar bears, have shown lower Hg concentrations related to reduced sea ice-based foraging and increased land-based foraging. How climate change influences Hg in Arctic freshwater fishes is not clear, but for lacustrine populations it may depend on lake-specific conditions, including interrelated alterations in lake ice duration, turbidity, food web length and energy sources (benthic to pelagic), and growth dilution. In several marine mammal and seabird species, tissue Hg concentrations have shown correlations with climate and weather variables, including climate oscillation indices and sea ice trends; these findings suggest that wind, precipitation, and cryosphere changes that alter Hg transport and deposition are impacting Hg concentrations in Arctic marine organisms. Ecological changes, including northward range shifts of sub-Arctic species and altered body condition, have also been shown to affect Hg levels in some populations of Arctic marine species. Given the limited number of populations and species studied to date, especially within Arctic terrestrial and freshwater systems, further research is needed on climate-driven processes influencing Hg concentrations in Arctic ecosystems and their net effects. Long-term pan-Arctic monitoring programs should consider ancillary datasets on climate, weather, organism ecology and physiology to improve interpretation of spatial variation and time trends of Hg in Arctic biota.
... Seasonality of observations of birds at sea during shipbased surveys corroborate the satellite-tracking results and also concur with earlier circumstantial evidence indicating that some birds from the Gulf of Alaska migrate north into the Bering Sea and Arctic Ocean (Day et al., 2011;. Once there, they likely remain in the northern portion of their range during winter and early spring to feed along the marginal ice zone and polynyas, similar to some other seabirds (Hunt, 1991;Divoky et al., 2016). Although some Kittlitz's Murrelets occupy ice-free habitats in each phase of their annual cycle, most associate with glacial ice or sea ice to some degree throughout the year, indicating a strong affiliation with ice or associated habitats, such as glacially modified mountains inland or glacial meltwaterinfluenced waters at sea. ...
Article
Full-text available
Kittlitz’s Murrelets (Brachyramphus brevirostris) nest during summer in glaciated or recently deglaciated (post-Wisconsin) landscapes. They forage in adjacent marine waters, especially those influenced by glacial meltwater. Little is known of their movements and distribution outside the breeding season. To identify post-breeding migrations of murrelets, we attached satellite transmitters to birds (n = 47) captured at sea in the Gulf of Alaska and Aleutian Islands during May – July 2009 – 15 and tracked 27 birds that migrated from capture areas. Post-breeding murrelets migrated toward the Bering Sea, with short periods of movement (median 2 d) separated by short stopovers (median 1 d). Travel speeds averaged 79.4 km d-1 (83.5 SD, 449.1 maximum). Five Kittlitz’s Murrelets tagged in Prince William Sound in May migrated to the Bering Sea by August and four continued north to the Arctic Ocean, logging 2500 – 4000 km of travel. Many birds spent 2‒3 weeks with little movement along coasts of the Alaska Peninsula or eastern Bering Sea during late August through September, also the pre-basic molt period. Ship-based surveys, many of which were conducted concurrently with our telemetry studies, confirmed that substantial numbers of Kittlitz’s Murrelets migrate into the Arctic Ocean during autumn. They also revealed that some birds spend winter and spring in the Bering Sea in association with ice-edge, polynya, or marginal ice zone habitats before returning to summer breeding grounds. We conclude that this species is best characterized as a sub-Arctic and Arctic species, which has implications for future risk assessments and threat mitigation.
... Even smaller-scale dynamic processes can have an extraordinary ecological value. Examples include floeedge systems and large ice-free polynyas used by associated species for foraging during winter (Divoky et al., 2016;Gilg et al., 2016). To ensure the long-term viability of seabird populations, wildlife managers benefit greatly from effective baseline "non-spatial" measures spanning jurisdictions and allowing for natural fluctuations and spatial shifts occurring at extended time scales in the order of decades and even hundreds of years. ...
Chapter
Protecting marine habitats for biodiversity is essential to ensure the long-term viability of these ecosystems, globally. Seabirds rely on healthy marine ecosystems and these relationships can span multiple jurisdictions in a single year, even within a single breeding season. The ecosystem dependency and political complexity requires a seabird practitioner to be aware of, understand and access a variety of approaches and spatial conservation tools to achieve seabird viability goals. These approaches include spatial planning, protected areas and other effective conservation measures as well as other tools, policy and legal instruments. In this chapter, marine spatial conservation measures are described, explored and contrasted in order to provide a solid foundation of theory and practice. The most commonly applied concepts and perspectives that are used currently are introduced as well as specific examples that have advanced the protection of seabirds in different parts of the world.
... Mandt's black guillemot, one of the few ice-associated Arctic seabirds, has been studied annually on Cooper Island, Alaska since 1975. The subspecies is reliant on sea ice throughout the year (Divoky et al. 2016) and the Cooper Island population is more dependent on food webs based on sea ice algae than other upper-trophic level predators in the region (Budge et al. 2008). Hatching of Mandt's Black Guillemots nestlings begins in mid-July with parents provisioning nestlings until early September. ...
Article
Full-text available
While decreases in Arctic sea ice affect all marine communities in the Arctic Basin, the effects are greatest on the cryopelagic ecosystem and species with critical life history stages dependent on the presence of sea ice. During the recent and ongoing period of rapid sea ice loss these species have been subject to spatial and temporal disruptions requiring behavioural plasticity. Mandt’s Black Guillemots (Cepphus grylle mandtii) is one of the few ice-obligate Arctic seabirds. Polar cod (Boreogadus saida) is their preferred prey. We monitored their prey selection and diving behaviour during the annual period of chick provisioning from 2011 to 2017, to assess their ability to respond to the now common seasonal loss of sea ice and increased water temperature in their nearshore foraging area. The percentage of polar cod fed to nestlings decreased with increasing SST, with fourhorn sculpin (Myoxocephalus quadricornis), a nearshore demersal, becoming common (20% of deliveries) with SST > 2.0 °C and comprising more than half of the prey when SST > 3.4 °C. This prey-switch coincided with a marked increase in dives and time underwater per day and a decrease in dive duration as birds switched to nearshore, benthic habitats. Sea ice is declining and SST increasing throughout the Arctic Basin and other upper-trophic level predators dependent on polar cod could be expected to be exhibiting similar prey-switching and modifications in foraging effort.
... As seabirds often face relatively high mortality during the non-breeding period compared to the breeding period, it is essential to characterize their winter foraging ecology to improve understanding of the potential effects of environmental changes and conservation threats to populations. In the Pacific Arctic, some seabird species remain in the ice-covered region throughout the year (Divoky et al., 2016). Still, the majority of Arctic-breeding seabirds migrate long distances and spend considerable time away from the Arctic region during the non-breeding period. ...
Article
Full-text available
Assessing impacts of environmental change on Arctic-breeding seabirds requires a better understanding of their year-round movement and foraging ecology. Here we examined the post-breeding movements and diving behavior of thick-billed (Uria lomvia) and common murres (U. aalge) breeding on St. Lawrence Island, northern Bering Sea, by using geolocators deployed in 2016 (n = 3, per species). During 2016–2019, we examined foraging niches and exposure to nutritional stress by using stable isotope signatures and corticosterone titers of blood and feather tissues (n = 60–96, per species). We found that thick-billed murres migrated to the Chukchi Sea in the fall and wintered in the western North Pacific, whereas common murres stayed in the eastern Bering Sea in the fall and wintered in the eastern North Pacific. Nutritional stress levels of breeding common murres were higher in 2017–2019, the period of historic low winter sea-ice extent, than in 2016. Higher nutritional stress levels of post-breeding thick-billed murres were associated with lower fall sea-ice extent in the Chukchi Sea. These results indicate that the loss of sea-ice might negatively affect murres breeding in the Pacific Arctic. Divergent migratory connectivity between the two murre species might also lead to different conservation threats both inside and outside the Arctic.
... The shifting distribution of krill may in turn influence the breeding success of top predators as these species are constrained in foraging duration and distance when rearing offspring (Lunn et al., 1993;Weimerskirch, 2007). Therefore, just as for predators which breed in high northern latitudes (Divoky, Douglas, & Stenhouse, 2016;Macias-Fauria & Post, 2018), there is a critical need for continued monitoring efforts to assess the effects of shifting prey distributions (due to climate change) on predator populations. ...
Article
Full-text available
Aim Marine protected areas can serve to regulate harvesting and conserve biodiversity. Within large multi‐use MPAs, it is often unclear to what degree critical sites of biodiversity are afforded protection against commercial activities. Addressing this issue is a prerequisite if we are to appropriately assess sites against conservation targets. We evaluated whether the management regime of a large MPA conserved sites (Key Biodiversity Areas, KBAs) supporting the global persistence of top marine predators. Location Southwest Atlantic Ocean. Method We collated population and tracking data (1,418 tracks) from 14 marine predator species (Procellariiformes, Sphenisciformes, Pinnipedia) that breed at South Georgia and the South Sandwich Islands, and identified hotspots for their conservation under the recently developed KBA framework. We then evaluated the spatiotemporal overlap of these sites and the different management regimes of krill, demersal longline and pelagic trawl fisheries operating within a large MPA, which was created with the intention to protect marine predator species. Results We identified 12 new global marine KBAs that are important for this community of top predators, both within and beyond the focal MPA. Only three species consistently used marine areas at a time when a potentially higher‐risk fishery was allowed to operate in that area, while other interactions between fisheries and our target species were mostly precluded by MPA management plans. Main conclusions We show that current fishery management measures within the MPA contribute to protecting top predators considered in this study and that resource harvesting within the MPA does not pose a major threat—under current climate conditions. Unregulated fisheries beyond the MPA, however, pose a likely threat to identified KBAs. Our approach demonstrates the utility of the KBA guidelines and multispecies tracking data to assess the contributing role of well‐designed MPAs in achieving local and internationally agreed conservation targets.
... Our results demonstrate the role that the marginal ice zone (MIZ, see [39])-a dynamic and biologically active region that transitions from the dense inner pack-ice zone to ice-free open ocean (e.g. [40,41])-plays in driving the distribution of Antarctic petrels during the winter months, as has been reported for other seabirds in the Arctic [42,43]. Birds remain within a large belt that stretches from the northern physical edge of the pack ice defined by satellite measurement (open water being defined here and elsewhere as cells where SIC was less than 15%; [44]) to the Polar Front in the North. ...
Article
Full-text available
There is a paucity of information on the foraging ecology, especially individual use of sea-ice features and icebergs, over the non-breeding season in many seabird species. Using geolocators and stable isotopes, we defined the movements, distribution and diet of adult Antarctic petrels Thalassoica antarctica from the largest known breeding colony, the inland Svarthamaren, Antarctica. More specifically, we examined how sea-ice concentration and free-drifting icebergs affect the distribution of Antarctic petrels. After breeding, birds moved north to the marginal ice zone (MIZ) in the Weddell sector of the Southern Ocean, following its northward extension during freeze-up in April, and they wintered there in April–August. There, the birds stayed predominantly out of the water (60–80% of the time) suggesting they use icebergs as platforms to stand on and/or to rest. Feather δ15N values encompassed one full trophic level, indicating that birds fed on various proportions of crustaceans and fish/squid, most likely Antarctic krill Euphausia superba and the myctophid fish Electrona antarctica and/or the squid Psychroteuthis glacialis. Birds showed strong affinity for the open waters of the northern boundary of the MIZ, an important iceberg transit area, which offers roosting opportunities and rich prey fields. The strong association of Antarctic petrels with sea-ice cycle and icebergs suggest the species can serve, year-round, as a sentinel of environmental changes for this remote region.
Article
Pigeon guillemots Cepphus columba are ubiquitous along the coasts of the eastern North Pacific, yet little is known about their winter migration patterns, habitat needs, and potential threats faced during the non-breeding period. We used 3 seasons of year-long light level data from tagged individuals to estimate the migration timing and winter residency of pigeon guillemots breeding on Southeast Farallon Island in California (USA). Light level data were combined with a movement model to estimate positions of tagged animals, revealing that individuals from this population undertook a coordinated coastal migration north in the fall, stopping at sites near Haida Gwaii in British Columbia (Canada), presumably during a flightless prebasic molt, before continuing north to stationary overwintering sites in coastal British Columbia and Southeast Alaska. Birds then made an uninterrupted migration south in the spring, returning to waters around Southeast Farallon in late March and early April. Wet/dry data indicated nocturnal resting on land during the breeding season and likely on the water throughout the non-breeding months. This is the first study to confirm the migratory patterns of pigeon guillemots from California, and highlights the importance of the waters of British Columbia and Southeast Alaska for the studied population and possibly other major populations of this species.
Article
Full-text available
Global warming and continued reduction in sea ice cover will result in longer open water duration in the Arctic, which is important for the shipping industry, marine mammals, and other components of the regional ecosystem. In this study we assess the length of open water duration in the Alaskan Arctic over the next few decades using the set of latest coupled climate models (CMIP5). The Alaskan Arctic, including the Chukchi and the Beaufort Sea, has been a major region of summer sea ice retreat since 2007. Thirty seven climate models from CMIP5 are evaluated and twelve are selected for composite projections based on their historical simulation performance. In the regions north of the Bering Strait (north of 70° N), future open-water duration shifts from a current 3-4 months to a projected near five months by 2040 based on the mean of the twelve seleted climate models. There is considerable north-south gradient in projected durations. Open water duration is about one month shorter along the same latitudes in the Beaufort Sea compared with that in the Chukchi Sea. Uncertainty is generally ±one month estimated from the range of model results. Open-water duration in the Alaskan Arctic expands quickly in these models over the next decades which will impact regional economic access and potentially alter ecosystems. Yet the northern Alaskan Arctic from January through May will remain sea ice covered into the second half of the century due to normal lack of sunlight.
Article
Full-text available
The ivory gull (Pagophila eburnea) is an endangered seabird that spends its entire year in the Arctic environment. In the past three decades, threats from various sources have contributed to a .70% decline in Canada. To assess the annual habitat needs of this species, we attached satellite transmitters to 12 ivory gulls on Seymour Island, Nunavut in 2010, which provided up to four breeding seasons of tracking data. Analysis of migratory behaviour revealed considerable individual variation of post-breeding migratory route selection. Ivory gulls traveled a median of 74 days during post-breeding migration, but only 18 days during pre-breeding migration. In contrast to predictions, ivory gulls did not use the Greenland coast during migratory periods. Ivory gulls overwintered near the ice edge in Davis Strait, but also used the Labrador Sea in late February and March. We suggest that the timing of formation and recession and extent of sea ice plays a large role in ivory gull distribution and migratory timing.
Article
Full-text available
We employed a "natural experiment" to evaluate the hypothesis that a major physical feature of high-latitude marine habitat, the percentage of the sea covered by pack ice, affects species composition among Antarctic seabirds. Our experiment entailed replicate transects through markedly altered physical habitat in the Scotia-Weddell Confluence: a series of storms caused the pack ice to advance and retreat rapidly and repeatedly over a 200-km-wide area. Regardless ofwhere their habitat moved, pack-ice and open-water species occurred at significantly higher densities in the ice and open-water habitats, respectively. There were no time lags in the response of species to habitat alteration. In addition, pack-ice and open-water species had identical diets regardless of where their preferred habitat was located. These results supported the hypothesis and showed that physical rather than biological variables affect species composition among pelagic assemblages of Antarctic sea-birds. Results supported the conclusion that a lack of appropriate adaptations constrain open-water species to reside away from the pack ice and that unremarkable prey availability fails to attract pack-ice species to open waters.
Article
We surveyed population-level sequence variation in part of the mitochondrial control region for three species including eight subspecies of Cepphus guillemots (Charadriiformes: Alcidae) to test specific predictions about mechanisms of population differentiation. We found that sequences of spectacled guillemots (C. carbo) were more closely related to those of pigeon guillemots (C. columba; both found in the Pacific Ocean) than to those of black guillemots (C. grylle; Arctic and Atlantic Oceans), despite dissimilarities in plumage between spectacled guillemots and the other species. Distributions of species and timing of divergence events suggest that speciation involved allopatric and microallopatric populations isolated by Pleistocene glaciers. Control region sequences were significantly differentiated among populations within species and suggest that gene flow is low; however, populations are probably not in genetic equilibrium, so these results probably reflect historical isolation of colonies. In contrast, phylogenetic relationships among sequences within species were poorly resolved, probably because of a combination of incomplete lineage sorting and contemporary gene flow. Indices of genetic diversity provided no suggestion of recent bottlenecks in most populations, although two populations apparently underwent recent severe bottlenecks. Genetic divergence among populations was not correlated with geographic distance, which argues against isolation by distance. Results of these analyses, combined with breeding distributions and timing of divergence events, suggest that populations diverged during isolation in glacial refugia. Our results are consistent with earlier hypotheses posed by Storer and Udvardy.
Article
The sympagic fauna (= ice fauna) of the Barents Sea was investigated on nine different cruises in 1982-1988. Each cruise lasted from two to five weeks. Sampling techniques were based on scuba diving. The abundant sympagic organisms were the polar cod (Boreogadus saida) and the three amphipods Apherusa glacialis, Onisimus sp. and Gammarus wilkitzkii. Mean biomass-values (wet weight) of the invertebrate sympagic fauna ranged from 0 to 2 g/m2. Values above 0.001 g/m2 were not recorded in five of the nine cruises. This is orders of magnitude lower than mean values recorded in multi-year ice north of Svalbard and in the Fram Strait where values between 1-10g/m2 are quite common. Apherusa glacialis seemed to have the best spreading capacity of the three most conspicuous amphipods. Gammarus wilkitzkii was most dependent on a passive transport with the ice. Sympagic amphipods play an important part in a food chain from microalgae to polar cod and marine birds in areas covered with ice, especially in areas with multi-year ice.
Article
We surveyed population-level sequence variation in part of the mitochondrial control region for three species including eight subspecies of Cepphus guillemots (Charadriiformes: Alcidae) to test specific predictions about mechanisms of population differentiation. We found that sequences of spectacled guillemots (C. carbo) were more closely related to those of pigeon guillemots (C. columba; both found in the Pacific Ocean) than to those of black guillemots (C. grylle; Arctic and Atlantic Oceans), despite dissimilarities in plumage between spectacled guillemots and the other species. Distributions of species and timing of divergence events suggest that speciation involved allopatric and microallopatric populations isolated by Pleistocene glaciers. Control region sequences were significantly differentiated among populations within species and suggest that gene flow is low; however, populations are probably not in genetic equilibrium, so these results probably reflect historical isolation of colonies. In contrast, phylogenetic relationships among sequences within species were poorly resolved, probably because of a combination of incomplete lineage sorting and contemporary gene flow. Indices of genetic diversity provided no suggestion of recent bottlenecks in most populations, although two populations apparently underwent recent severe bottlenecks. Genetic divergence among populations was not correlated with geographic distance, which argues against isolation by distance. Results of these analyses, combined with breeding distributions and timing of divergence events, suggest that populations diverged during isolation in glacial refugia. Our results are consistent with earlier hypotheses posed by Storer and Udvardy.
Article
observed rapid loss of thick multiyear sea ice over the last 7 years and the September 2012 Arctic sea ice extent reduction of 49% relative to the 1979-2000 climatology are inconsistent with projections of a nearly sea ice-free summer Arctic from model estimates of 2070 and beyond made just a few years ago. Three recent approaches to predictions in the scientific literature are as follows: (1) extrapolation of sea ice volume data, (2) assuming several more rapid loss events such as 2007 and 2012, and (3) climate model projections. Time horizons for a nearly sea ice-free summer for these three approaches are roughly 2020 or earlier, 2030 ± 10 years, and 2040 or later. Loss estimates from models are based on a subset of the most rapid ensemble members. It is not possible to clearly choose one approach over another as this depends on the relative weights given to data versus models. Observations and citations support the conclusion that most global climate model results in the CMIP5 archive are too conservative in their sea ice projections. Recent data and expert opinion should be considered in addition to model results to advance the very likely timing for future sea ice loss to the first half of the 21st century, with a possibility of major loss within a decade or two.