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1 quilibrium body temperature of an individual ectotherm.
2 the overall cost of growth for an individual ectotherm.
3 Peyer patches but not the O-MALT of birds or ectotherms.
4 -visual roles, including thermoregulation in ectotherms.
5 limits among related species of terrestrial ectotherms.
6 lly rather than linearly with temperature in ectotherms.
7 nding of the relative thermal sensitivity of ectotherms.
8 at these results are general for terrestrial ectotherms.
9 responses have been observed for terrestrial ectotherms.
10 uickly than heat tolerance in endotherms and ectotherms.
11 , all stem mammaliamorphs were most probably ectotherms.
12 development affect a wide range of traits in ectotherms.
13 temperatures is beneficial or deleterious to ectotherms.
14 ucocorticoid concentrations, particularly in ectotherms.
15 traits through which climate impacts marine ectotherms.
16 particularly for detecting small mammals and ectotherms.
17 olour lightness-environment relationships in ectotherms.
18 s evolved several times in animals including ectotherms.
19 polewards to a greater degree than temperate ectotherms.
20 al and ecological processes, particularly in ectotherms.
21 fects of chronic, sublethal warming on small ectotherms.
22 incipal thermoregulator of the brain also in ectotherms.
23 is known to influence mortality patterns in ectotherms.
24 eat-related challenges for polar terrestrial ectotherms.
25 ressional wetlands are temperature-sensitive ectotherms.
26 olic rate and hence aerobic scope of aquatic ectotherms.
27 uring cold exposure in this diverse group of ectotherms.
28 ver broader temperature ranges than tropical ectotherms.
29 e to environmental conditions, especially in ectotherms.
30 that of oxygen consumption in endotherms and ectotherms.
31 of Lake Tanganyika fishes and other tropical ectotherms.
32 mammals, lineages of LMP7 are restricted to ectotherms.
33 d-across geographic ranges of several marine ectotherms.
34 being considerably faster in endotherms than ectotherms.
35 ic demands and energy requirements of marine ectotherms.
36 eed the physiological thermal limits of most ectotherms.
40 ass) and quality (nutrient content) and that ectotherm access to food increases with temperature.
42 Here, we compile thermal-tolerance limits of ectotherms across a wide range of latitudes and elevatio
43 eir upper thermal limits than do terrestrial ectotherms across all latitudes-but that this is the cas
44 solved this apparent paradox by showing that ectotherm activity generates microclimatic deviations la
47 re the potential impact of global warming on ectotherm ageing through its effects on reactive oxygen
49 We compare how major groups of vertebrate ectotherms (amphibians) and endotherms (birds) respond t
52 mance is influenced by thermal conditions in ectotherms and an increase in temperature by only 2 C is
54 were intermediate to those of endotherms and ectotherms and closest to those of extant mesotherms.
55 e variation in the thermal limits of aquatic ectotherms and could adversely affect wild populations i
57 ponsible for tuberculosis-like infections in ectotherms and is an occasional opportunistic human path
58 sonal life cycle regulation evolves in urban ectotherms and may contribute to ecoevolutionary dynamic
59 ming will limit the aerobic scope of aquatic ectotherms and may place a greater metabolic burden on l
60 ions that widespread extinctions of tropical ectotherms, and tropical forest lizards in particular, w
65 There is increasing evidence that aquatic ectotherms are especially vulnerable to global warming s
67 he limited data available suggest that polar ectotherms are more sensitive to warming than previously
73 provide a physiological basis for projecting ectotherm body size responses to climate change from mic
74 tal warming is associated with reductions in ectotherm body sizes, suggesting that larger individuals
75 n apparent general decrease in body sizes of ectotherms, both across and within taxa, especially in a
76 mergence is widely reported in high-latitude ectotherms, but a significant number of species exhibit
77 tion can set heat tolerance for some aquatic ectotherms, but only at unrealistic lethal temperatures
78 ht to lead to increased immune reactivity in ectotherms, but we found that the effect of temperature
80 ing can induce a cost-of-living "squeeze" in ectotherms by increasing energetic expenditures while re
81 ate warming is expected to benefit temperate ectotherms by lengthening the summer growing season, dec
84 y the partitioning of the climatic niche, as ectotherms can rely on water availability and thermoregu
86 if we aim to understand or even predict how ectotherm communities will react to global warming and n
89 ere, we use datasets of predatory vertebrate ectotherms (crocodilians, turtles, lizards and fishes) t
90 inting, swimming, and jumping performance of ectotherms decreases by at least 33% over a 10 degrees C
92 that cannot regulate their body temperature (ectotherms) depends on their ability to increase the flu
93 n exert strong natural selection on tropical ectotherms, despite their ability to thermoregulate beha
94 Controlling for phylogeny and body size, ectotherms display a higher diversity of aging rates com
96 evious findings using air temperatures, most ectotherms do not have a physiological thermal-safety ma
100 pply affecting aerobic metabolism of aquatic ectotherms, ecological theories such as the metabolic th
101 ure dynamics could provide new insights into ectotherm ecology both now and in response to future cli
103 The model fits metabolic rates of microbes, ectotherms, endotherms (including those in hibernation),
104 trends in temperature variability: tropical ectotherms evolve to be 'thermal specialists' because th
106 mpute a cumulative 'metabolic currency' that ectotherms expend (or accumulate) before reaching their
112 ncubation temperatures for birds and aquatic ectotherms (fish, amphibians, aquatic insects and zoopla
114 ted in a given thermal environment, and that ectotherm food chain lengths should increase with increa
115 he thermal tolerance of 17 species of marine ectotherm from tropical, warm temperate and cold tempera
116 data on geographic variation in lifespan in ectotherms from around the globe to determine how much o
118 But, it prevents both tropical and temperate ectotherms from maintaining sink populations in localiti
119 scuss candidate mechanisms that could buffer ectotherms from the potentially negative consequences of
120 , observed thermal limits may differ between ectotherms from the same environment, challenging this t
125 tions for a desert site predict that shallow ectotherms have increased opportunities for mid-winter a
130 cold temperatures, a particular challenge in ectotherms, however, relies on a deliberate strategy com
131 atory warming experiments of diverse aquatic ectotherms (i.e., the "temperature-size rule" [TSR]).
132 the minimal maintenance metabolic rate of an ectotherm in a post-absorptive and inactive state and ca
133 o found that even among highly mobile marine ectotherms in a global warming hotspot, few species are
134 emperature within species in a wide range of ectotherms in both controlled laboratory experiments and
135 ch as cetaceans might shift more slowly than ectotherms in response to warming and would primarily fo
139 n may be particularly likely for short-lived ectotherms, including many pest, pathogen, and vector sp
140 for assessing hydrological needs of aquatic ectotherms, including the parasite-host relationship, wh
141 he general contention that for high-latitude ectotherms, increasing spring temperatures associated wi
143 behind the response is well established for ectotherms inhabiting aquatic environments: as higher te
145 n temperature on the aerobic scope of marine ectotherms is a primary driver of migrating biodiversity
147 tly incorporates mechanistic descriptions of ectotherm life history trait responses to temperature.
149 mpacts of future warming trends on temperate ectotherms' life cycle and population persistence are la
150 l warming as an independent factor affecting ectotherms' life history in the context of global climat
152 hanges in activities, may help buffer forest ectotherms like butterflies from microclimate changes in
155 a critical adaptation for insects and other ectotherms living in thermally variable environments.
158 ze how climate-driven telomere shortening in ectotherms may accumulate across generations and generat
159 remain difficult to predict, in part because ectotherms may adapt or acclimate to novel conditions or
160 increases in global temperature, lifespan of ectotherms may be substantially shortened in the future.
162 lations underlying the thermal physiology of ectotherms might influence their responses to the two ma
163 ndings highlight the complex trade-offs that ectotherms must navigate to balance behavioural thermore
164 stantially lower oxygen consumption rates of ectotherms of a given body mass relative to those of end
168 ical thermal-tolerance limits of terrestrial ectotherms often exceed local air temperatures, implying
172 mal melanism theory states that dark-colored ectotherm organisms are at an advantage at low temperatu
173 gical trade-off involving the depth at which ectotherms overwintered: on warm days, only shallow rept
176 n extraordinary clade to test these rules in ectotherms owing to their exemplary fossil record and th
179 Developing a thorough understanding of how ectotherm physiology adapts to different thermal environ
180 hange, more work is needed to understand how ectotherm physiology relates to microclimatic temperatur
181 These results suggest that predictions of ectotherm population viability based on rm may be valid
183 ng population persistence depends on whether ectotherm populations can achieve a stable age/stage dis
185 predictions, both terrestrial endotherm and ectotherm predators have significantly positive predator
187 ture during development of distantly related ectotherms ranging from the insect Drosophila melanogast
189 ral and internal warmth sensors in this tiny ectotherm reminiscent of thermoregulatory systems in lar
190 wer metabolic rates per gram of body mass in ectotherms resulted in endotherms and ectotherms having
191 ormance curves (TPCs), which quantify how an ectotherm's body temperature (Tb ) affects its performan
194 n trait response data predicts that tropical ectotherms should be able to expand their distributions
196 threaten tropical ectotherms while temperate ectotherms should resist or even benefit from higher tem
197 of these changes may be especially acute on ectotherms since they have limited capacities to use met
198 ture and rainfall may thus mold gradients of ectotherm size, with consequences for the structure and
199 etermines the upstream extent of the aquatic ectotherm smallmouth bass (Micropterus dolomieu) in two
201 s both confirm and confound expectations for ectotherm species affected by climate warming: an increa
202 cts of future climates on a model vertebrate ectotherm species using a large-scale warming experiment
207 ; however, comparable adaptations in aquatic ectotherms, such as fishes, have not been as extensively
208 e conditions are challenging for soft-bodied ectotherms, such as termites, to survive in, let alone b
210 kton size spectrum, the larger end comprises ectotherms that are often studied at the species, or gro
211 metabolic differences between endotherms and ectotherms that drive trophic and competitive interactio
214 pears to be much greater for endotherms than ectotherms, the reasons for which are not fully understo
216 tal Ratios in different aquatic invertebrate ectotherms: the freshwater model species Daphnia magna,
217 ng the life histories of long-lived tropical ectotherms: the seemingly incongruent combination of ext
223 r associated fauna, which may benefit marine ectotherms, though temperature differentials were narrow
224 oved forecast accuracy in 18 of 19 empirical ectotherm time series (by 19% on average), with the larg
225 To evaluate the capacity of a widespread ectotherm to anticipated environmental changes, we condu
228 es of molecular variation in the response of ectotherms to environmental temperature variation in the
231 ependent, allows both tropical and temperate ectotherms to track warming-induced changes in their the
233 otherms, we show that the temperature ranges ectotherms tolerate (the difference between lower and up
234 nternal energy to regulate body temperature, ectotherms typically regulate body temperature behaviora
236 ing rates and longevity across wild tetrapod ectotherms, using data from 107 populations (77 species)
237 s of trophic position based on delta(15)N in ectotherm vertebrates with large size ranges, may be ina
238 investigating the gut microbial diversity of ectotherms, we lack an understanding of how environmenta
240 nimodal thermal performance is ubiquitous in ectotherms, we suggest that this may be a general explan
243 ts also reveal deep-time climate legacies in ectotherms, whereby orders that originated in cold paleo
244 the majority of animals and vertebrates are ectotherms, which often experience fluctuations in body
245 emperatures are particularly challenging for ectotherms, which use both basal thermotolerance and acc
246 obal warming will severely threaten tropical ectotherms while temperate ectotherms should resist or e
247 most biodiversity on the planet consists of ectotherms whose body temperature depends on the environ
248 ty and distribution of species, particularly ectotherms whose body temperatures depend on environment
249 ch variation may be especially important for ectotherms whose body temperatures, and consequently, ph
250 l model that predicts that infection risk in ectotherms will decrease as the difference between host
251 forecasts of the impact of climate change on ectotherms will require an understanding of the genetic
253 e or time in N. unicornis and possibly other ectotherms with the combination of longevity and asympto
254 and acidification act concurrently on marine ectotherms with the potential for detrimental, synergist
256 have important physiological implications in ectotherms, with darker species having greater heating r
257 ngs of the American alligator, an amphibious ectotherm without air sacs, which suggests that this pat
258 influences the distribution and diversity of ectotherms, yet in natural settings, interactions betwee
259 sk among three age classes in a cold-adapted ectotherm (Zootoca vivipara) facing warming-induced exti