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1 for flightless wing-propelled diving birds (penguins).
2 change is a significant risk for the emperor penguin.
3 vide satisfactory conditions for the emperor penguin.
4 as illustrated by recent work on rabbits and penguins.
5 n conductance than those from never-immersed penguins.
6 ula's largest breeding populations of gentoo penguins.
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 ss and observation error to all known Adelie penguin abundance data (1982-2015) in the Antarctic, cov
13 declines, we suggest that declines in Adelie penguins along the WAP are more likely due to direct and
15 ami, and bitter tastes have been lost in all penguins, an order of aquatic flightless birds originati
16 a (WAP) is coincident with increasing gentoo penguin and decreasing Adelie penguin populations, sugge
18 itude Antarctic seabirds (Adelie and Emperor penguins and snow petrels) indicate that winter sea-ice
19 ertical foraging ranges of Adelie and gentoo penguins, and found that krill selected for habitats tha
23 reenhouse gases (GHGs) increase, and emperor penguins (Aptenodytes forsteri) are extremely sensitive
24 im was to estimate the population of emperor penguins (Aptenodytes fosteri) using a single synoptic s
25 cs are driven by stochastic processes.Adelie penguins are a key Antarctic indicator species, but data
29 re on current trends, we see Southern gentoo penguins are responding to current warming as they did d
30 arctic Peninsula, favoring generalist gentoo penguins as climate change 'winners', while Adelie and c
31 estimated the breeding population of emperor penguins at each colony during 2009 and provide a popula
32 light of this new structure and of the king penguin AvBD103b defensin structure, the consensus seque
33 heir dimensions were similar to those of non-penguin avian taxa and that the feathering may have been
34 n early penguin cranial osteology, trends in penguin body size, and the evolution of the penguin flip
36 We used true presence-absence data on Adelie penguin breeding colonies to estimate past and future ch
39 ate total GHG emission potential from Adelie penguin colonies during breeding seasons in 1983 and 201
41 n conducted to determine the GHG fluxes from penguin colonies, however, at regional scale, there is s
42 we project that one-third of current Adelie penguin colonies, representing ~20% of their current pop
44 tailed biogeochemical analyses to track past penguin colony change over the last 8,500 years on Ardle
45 nstead, at least three of the five phases of penguin colony expansion were abruptly ended by large er
48 pecies provide critical information on early penguin cranial osteology, trends in penguin body size,
51 ate an abrupt shift to lower-trophic prey in penguin diets within the past approximately 200 years.
52 following summer, which is evident in Adelie penguin diets, thus demonstrating tight trophic coupling
53 their terrestrial call, the offshore call of penguins during their foraging trips has been poorly stu
54 hydrography and foraging patterns of Adelie penguins during these switching tidal regimes suggest th
55 es of delta13C and delta15N values of Adelie penguin eggshell from abandoned colonies located in thre
56 amyxovirus recently isolated from rockhopper penguins (Eudyptes chrysocome) suggested that this virus
59 edators-sharks, bony fishes, sea turtles and penguins-exhibit Levy-walk-like behaviour close to a the
60 We propose that this isolate, named APMV10/penguin/Falkland Islands/324/2007, be the prototype viru
62 ntrast, the dark black-brown color of extant penguin feathers is generated by large, ellipsoidal mela
75 o make radio-frequency identifications, wild penguins had significantly lower and shorter stress resp
79 o their sensitivity to environmental change, penguins in Antarctica are widely used as bio-indicators
80 important implications for the use of Adelie penguins in Southern Ocean feedback management, and sugg
82 first description of the vocal behaviour of penguins in the open ocean and discuss the function of t
83 story and population structure of Pygoscelis penguins in the Scotia Arc related to climate warming af
84 ains why populations of Adelie and chinstrap penguins increased after competitors (fur seals, baleen
86 e middle and late Eocene of Peru reveal that penguins invaded low latitudes >30 million years earlier
90 ore, adaptive thermogenesis in juvenile king penguins is linked to two separate mechanisms of uncoupl
93 ndonment of the colonies, and we believe the penguins migrated from the coastal area of mid Cape Bird
98 nt profiles, we reconstructed the historical penguin population change at Cape Bird, Ross Island, for
99 krill is one of the major drivers of Adelie penguin population declines, we suggest that declines in
101 sent a population projection for the emperor penguin population of Terre Adelie, Antarctica, by linki
104 ng the contemporary period, declining Adelie penguin populations experienced more years with warm sea
106 t attributes both increases and decreases in penguin populations to changes in the abundance of their
107 The main reasons for the increase in Adelie penguin populations were attributed to increase in tempe
108 literature that global and regional emperor penguin populations will be affected by changing climate
109 reasing gentoo penguin and decreasing Adelie penguin populations, suggesting that competition for foo
111 emonstrate this mechanism is not controlling penguin populations; populations of both ice-loving Adel
112 in their dominant frequency and length, and penguins produced calls of different lengths in successi
114 atry was previously confirmed for the Adelie penguin (Pygoscelis adeliae) during a period of stable e
116 nalysis (OBIA) method to estimate the Adelie penguin (Pygoscelis adeliae) population based on aerial
117 We deployed an animal-borne camera on gentoo penguins (Pygoscelis papua) and recorded their foraging
118 a, places the new species outside the extant penguin radiation (crown clade: Spheniscidae) and suppor
120 earing niche spaces for the three Pygoscelis penguin species and used a maximum entropy approach (Max
122 MJ was isolated from the choana of a jackass penguin (Spheniscus demersus) with recurrent mucocaseous
123 llite tracked postnatal dispersal in African penguins (Spheniscus demersus) from eight sites across t
125 d gentoo penguin foraging areas, four gentoo penguins switched foraging behavior by foraging at deepe
127 Skeletal muscle mitochondria isolated from penguins that had never been immersed in cold water show
128 30 y of field studies and recent surveys of penguins throughout the WAP and Scotia Sea demonstrate t
129 used three different groups of juvenile king penguins to investigate the mitochondrial basis of avian
130 e of their 'two-voice' calls enables emperor penguins to locate their mates and chicks under some of
131 ian state-space and habitat models show that penguins traversed thousands of square kilometers to are
133 nvert these classified areas into numbers of penguins using a robust regression algorithm.We found fo
134 e level confirmed that APMV2, APMV8, and the penguin virus all were sufficiently divergent from each
135 n addition, antiserum generated against this penguin virus did not inhibit the HA of representative v
137 natomical constraints that influence nesting penguin vocalisations from a source-filter perspective,
138 edators in this region, Adelie and chinstrap penguins were never directly harvested by man; thus, the
140 We infer from our results that macaroni penguins will most likely be negatively impacted by an i
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