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1 s, cetaceans, sirenians, flying seabirds and penguins).
2 for flightless wing-propelled diving birds (penguins).
3 change is a significant risk for the emperor penguin.
4 vide satisfactory conditions for the emperor penguin.
5 es showing rhythmic accelerando, the African penguin.
6 on the source of marine MeHg accumulated by penguin.
7 trategy which limits competition with Adelie penguins.
8 itive exclusion of Adelie penguins by gentoo penguins.
9 stroke, essentially the same as turtles and penguins.
10 er wing-propelled diving seabirds, including penguins.
11 as illustrated by recent work on rabbits and penguins.
12 n conductance than those from never-immersed penguins.
13 arine and coastal ecosystems alongside early penguins.
14 vide an important molting habitat for Adelie penguins.
15 shape the diversity of mitogenomes in gentoo penguins.
16 ations in the Scotia Arc, focusing on gentoo penguins.
17 roach for microplastic analyses in Antarctic penguins.
18 ivity for shallow- versus deep-diving gentoo penguins.
19 rface convergent features compared to gentoo penguins.
20 ed to affect krill-dependent predators, like penguins.
21 ula's largest breeding populations of gentoo penguins.
23 n the foraging efficiency of breeding Adelie penguins, a relatively short-lived seabird species, in o
25 ss and observation error to all known Adelie penguin abundance data (1982-2015) in the Antarctic, cov
27 for quantifying future changes in Chinstrap penguin abundance, sheds new light on the environmental
30 e for an endangered species, implicates both penguin age and the presence of a potential bacterial pa
31 tochondrial efficiency seem to occur in king penguins, allowing them to cope with their stochastic an
32 declines, we suggest that declines in Adelie penguins along the WAP are more likely due to direct and
34 ami, and bitter tastes have been lost in all penguins, an order of aquatic flightless birds originati
35 a (WAP) is coincident with increasing gentoo penguin and decreasing Adelie penguin populations, sugge
38 Corynebacterium spp. causing oral lesions in penguins and a lesser-known genus, Mergibacter within Fa
39 allochrony in sympatric Adelie and chinstrap penguins and explores its resilience to climate change.
40 ampling coincided with bio-logging of Adelie penguins and observations of other air-breathing predato
41 on temporal trends and potential effects on penguins and other organisms in the Antarctic marine foo
43 many regions on Earth [4-7], and input from penguins and seals is associated with increased plant gr
44 itude Antarctic seabirds (Adelie and Emperor penguins and snow petrels) indicate that winter sea-ice
46 ertical foraging ranges of Adelie and gentoo penguins, and found that krill selected for habitats tha
47 d to reliably estimate energy expenditure in penguins, and we provide calibration equations for estim
50 ollected opportunistically from wild emperor penguins Aptenodytes forsteri, which exemplify capital b
51 ine and 16 perfluoroalkyl pollutants in king penguins Aptenodytes patagonicus during the breeding and
52 we project the dynamics of all known emperor penguin (Aptenodytes forsteri) colonies under new climat
54 reenhouse gases (GHGs) increase, and emperor penguins (Aptenodytes forsteri) are extremely sensitive
56 for-space substitutions (TFSS) using emperor penguins (Aptenodytes forsteri) as the focal species.
58 im was to estimate the population of emperor penguins (Aptenodytes fosteri) using a single synoptic s
60 cs are driven by stochastic processes.Adelie penguins are a key Antarctic indicator species, but data
65 re on current trends, we see Southern gentoo penguins are responding to current warming as they did d
66 ctive population sizes (N (e) ) confirm that penguins are sensitive to climate shifts, as represented
68 arctic Peninsula, favoring generalist gentoo penguins as climate change 'winners', while Adelie and c
69 study highlights the potential of migratory penguins as vectors of antimicrobial-resistant microorga
70 es in krill availability, relative to gentoo penguins, as evinced by their declining population trend
71 estimated the breeding population of emperor penguins at each colony during 2009 and provide a popula
72 light of this new structure and of the king penguin AvBD103b defensin structure, the consensus seque
73 heir dimensions were similar to those of non-penguin avian taxa and that the feathering may have been
74 n early penguin cranial osteology, trends in penguin body size, and the evolution of the penguin flip
75 nerate useful short-term forecasts of Adelie penguin breeding abundance will be extremely limited.
77 We used true presence-absence data on Adelie penguin breeding colonies to estimate past and future ch
83 ns apparently remain favorable for Chinstrap penguins, cannot be assessed against a historical benchm
85 trace Hg accumulation in Adelie and emperor penguin chicks from four breeding colonies in Antarctica
86 Interspecific variation of Delta(199)Hg in penguin chicks reflects the distinct foraging habitats a
87 ys of emperor penguin chicks, whereas Adelie penguin chicks showed different internal responses depen
88 hylation in the liver and kidneys of emperor penguin chicks, whereas Adelie penguin chicks showed dif
91 ate total GHG emission potential from Adelie penguin colonies during breeding seasons in 1983 and 201
94 icting the abundance distribution of emperor penguin colonies with a correlation coefficient of 0.58.
95 n conducted to determine the GHG fluxes from penguin colonies, however, at regional scale, there is s
96 we project that one-third of current Adelie penguin colonies, representing ~20% of their current pop
99 tailed biogeochemical analyses to track past penguin colony change over the last 8,500 years on Ardle
100 nstead, at least three of the five phases of penguin colony expansion were abruptly ended by large er
102 prior occupation of the Cape Hallett Adelie penguin colony site by southern elephant seal (Mirounga
106 includes various dispersal behaviors so that penguins could modulate climate effects through movement
107 pecies provide critical information on early penguin cranial osteology, trends in penguin body size,
112 d beta diversity of the microbial community: penguin developmental stage, sampling location, and C. p
113 te strong selective pressures, we found that penguins did not adapt morphologically to long-term envi
115 ata reveal spatiotemporal patterns of Adelie penguin diet, including spatial patterns in consumption
116 ate an abrupt shift to lower-trophic prey in penguin diets within the past approximately 200 years.
117 following summer, which is evident in Adelie penguin diets, thus demonstrating tight trophic coupling
120 s likely to have been associated with gentoo penguin diversification across the Southern Ocean and to
122 their terrestrial call, the offshore call of penguins during their foraging trips has been poorly stu
123 hydrography and foraging patterns of Adelie penguins during these switching tidal regimes suggest th
124 es of delta13C and delta15N values of Adelie penguin eggshell from abandoned colonies located in thre
125 amyxovirus recently isolated from rockhopper penguins (Eudyptes chrysocome) suggested that this virus
130 edators-sharks, bony fishes, sea turtles and penguins-exhibit Levy-walk-like behaviour close to a the
132 .27 to 1.15 per mille), whereas only emperor penguins exhibited the lowest delta(202)Hg in the liver
134 We propose that this isolate, named APMV10/penguin/Falkland Islands/324/2007, be the prototype viru
137 ntrast, the dark black-brown color of extant penguin feathers is generated by large, ellipsoidal mela
150 most divergent lineages, the eastern gentoo penguin from Crozet and Marion Islands and the southern
153 ctors that define the range limits of Adelie penguins, further establishing this iconic marine predat
154 rate of foraging dives per hour equated to a penguin gaining an average 170 g of mass, over the cours
155 yzing population genomic datasets spanning 3 penguin genera (Eudyptes, Pygoscelis, and Aptenodytes).
156 asma (n = 128) from eight species, including penguins, giant petrels, skuas, albatrosses, and shearwa
160 o make radio-frequency identifications, wild penguins had significantly lower and shorter stress resp
161 udy suggests that local adaptation of gentoo penguins has emerged as a response to environmental vari
165 occupied similar marine trophic levels, with penguins having larger isotopic niche spaces in 2014 whe
166 e (Pygoscelis adeliae) and gentoo (P. papua) penguins in a known biological hotspot near Palmer Deep
167 o their sensitivity to environmental change, penguins in Antarctica are widely used as bio-indicators
168 in some environmental contexts, and smaller penguins in others, ultimately mitigating their ability
170 important implications for the use of Adelie penguins in Southern Ocean feedback management, and sugg
172 first description of the vocal behaviour of penguins in the open ocean and discuss the function of t
173 story and population structure of Pygoscelis penguins in the Scotia Arc related to climate warming af
175 ains why populations of Adelie and chinstrap penguins increased after competitors (fur seals, baleen
178 e middle and late Eocene of Peru reveal that penguins invaded low latitudes >30 million years earlier
183 ore, adaptive thermogenesis in juvenile king penguins is linked to two separate mechanisms of uncoupl
184 by 2100, thus the total abundance of emperor penguins is projected to decline by at least 81% relativ
185 The specialized foraging niche of chinstrap penguins likely renders them more sensitive to changes i
187 from nine locations spanning all four gentoo penguin lineages, we demonstrated lineage-specific nucle
190 than the mixed layer, suggesting that Adelie penguins may be more responsive to dynamic surface conve
191 logic specialization of diving birds such as penguins may have involved adaptive changes in convectiv
194 ndonment of the colonies, and we believe the penguins migrated from the coastal area of mid Cape Bird
200 icted to the upper mixed layer, while gentoo penguins often foraged much deeper than the mixed layer,
206 local harvest rates, future observations of penguin performance are predicted to be below the long-t
207 rs of monitoring data, we show that expected penguin performance was reduced when local harvest rates
208 nt profiles, we reconstructed the historical penguin population change at Cape Bird, Ross Island, for
209 krill is one of the major drivers of Adelie penguin population declines, we suggest that declines in
210 ht on the environmental drivers of Chinstrap penguin population dynamics in Antarctica, and contribut
213 sent a population projection for the emperor penguin population of Terre Adelie, Antarctica, by linki
216 ociated with seal presence, but only emperor penguin population size had a strong negative relationsh
217 ng the contemporary period, declining Adelie penguin populations experienced more years with warm sea
218 e profiles in faecal samples from pygoscelid penguin populations in the Scotia Arc, focusing on gento
220 t attributes both increases and decreases in penguin populations to changes in the abundance of their
221 The main reasons for the increase in Adelie penguin populations were attributed to increase in tempe
222 literature that global and regional emperor penguin populations will be affected by changing climate
223 reasing gentoo penguin and decreasing Adelie penguin populations, suggesting that competition for foo
225 emonstrate this mechanism is not controlling penguin populations; populations of both ice-loving Adel
228 in their dominant frequency and length, and penguins produced calls of different lengths in successi
230 y on time series for abundance of the Adelie penguin Pygoscelis adeliae and explored the occurrence o
231 microplastics in a top predator, the gentoo penguin Pygoscelis papua from the Antarctic region (Bird
233 atry was previously confirmed for the Adelie penguin (Pygoscelis adeliae) during a period of stable e
235 nalysis (OBIA) method to estimate the Adelie penguin (Pygoscelis adeliae) population based on aerial
236 ple yielded hundreds of reads from chinstrap penguin (Pygoscelis antarcticus) and Weddell seal (Lepto
237 ve global population assessment of Chinstrap penguins (Pygoscelis antarctica) at 3.42 (95th-percentil
238 We deployed an animal-borne camera on gentoo penguins (Pygoscelis papua) and recorded their foraging
240 a, places the new species outside the extant penguin radiation (crown clade: Spheniscidae) and suppor
241 n molting (3.3-5.7 ng g(-1) ww) and breeding penguins (range of 4.2-7.3 ng g(-1) wet weight, ww).
242 Agreement objectives are met, viable emperor penguin refuges will exist in Antarctica, and only 19% a
244 rection over the course of return paths, the penguins' return paths were consistently S-shaped but st
245 icant differences in microplastic numbers in penguin scats between the two regions were detected.
248 servations of other air-breathing predators (penguins, seals, and whales), all of which were competin
249 clining demographic histories inferred for 4 penguin species (northern rockhopper, western rockhopper
250 the observed population declines of the two penguin species across the Western Antarctic Peninsula.
251 earing niche spaces for the three Pygoscelis penguin species and used a maximum entropy approach (Max
254 in deeper time, the most common (in 11 of 18 penguin species) being an increased N (e) between 40 and
257 s bracket the phylogenetic interval in which penguin-specific changes in Hb function would have evolv
258 MJ was isolated from the choana of a jackass penguin (Spheniscus demersus) with recurrent mucocaseous
259 of antimicrobial resistance in a Magellanic Penguin (Spheniscus magellanicus) rescued off the coast
260 e gut microbiome of the endangered Galapagos penguin (Spheniscus mendiculus) with the goals of charac
261 llite tracked postnatal dispersal in African penguins (Spheniscus demersus) from eight sites across t
262 set following the fates of 53,959 Magellanic penguins (Spheniscus magellanicus) to investigate whethe
263 allow-diving Adelie and deeper-diving gentoo penguins strongly selected for surface convergent featur
264 shifting isotopic baseline supporting gentoo penguins suggests a concurrent increase in coastal produ
266 d gentoo penguin foraging areas, four gentoo penguins switched foraging behavior by foraging at deepe
268 l-place foragers such as the Pygoscelis spp. penguins that breed along the WAP during the austral sum
270 Skeletal muscle mitochondria isolated from penguins that had never been immersed in cold water show
271 the greatest impacts on species like little penguins that have relatively restricted foraging ranges
273 30 y of field studies and recent surveys of penguins throughout the WAP and Scotia Sea demonstrate t
275 nalysis of range-wide survey data for Adelie penguins to characterize multidecadal and annual effects
276 used three different groups of juvenile king penguins to investigate the mitochondrial basis of avian
277 e of their 'two-voice' calls enables emperor penguins to locate their mates and chicks under some of
278 population responses in migratory Magellanic penguins to long-term changes in climate means and varia
279 is antarctica) and gentoo (Pygoscelis papua) penguins to nearly 100 y of shared environmental change
280 nce in Galliformes, ratites, passerines, and penguins, together representing the three major taxa of
281 ian state-space and habitat models show that penguins traversed thousands of square kilometers to are
285 nvert these classified areas into numbers of penguins using a robust regression algorithm.We found fo
286 e level confirmed that APMV2, APMV8, and the penguin virus all were sufficiently divergent from each
287 n addition, antiserum generated against this penguin virus did not inhibit the HA of representative v
289 natomical constraints that influence nesting penguin vocalisations from a source-filter perspective,
290 We show that lineage diversification in penguins was largely driven by changing climatic conditi
293 edators in this region, Adelie and chinstrap penguins were never directly harvested by man; thus, the
294 tactic bacteria or the temperature field for penguins-while urging for an optimal resource value.
296 We infer from our results that macaroni penguins will most likely be negatively impacted by an i
298 cceleration loggers on 58 free-living Adelie penguins with doubly labelled water (DLW) measurements o
301 mammals and birds such as tigers, pandas and penguins, yet the bulk of animal life, whether measured