2018
DOI: 10.1016/j.jtherbio.2018.09.015
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From conceptual to computational: Cost and benefits of lizard thermoregulation revisited

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Cited by 5 publications
(5 citation statements)
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“…During the day, lizards were more effective thermoregulators where thermal quality was lower (high elevation). These results are consistent with those of a global analysis of the effect of thermal quality on thermoregulation of lizards that indicated that poor thermal quality led to higher effectiveness of thermoregulation (Blouin‐Demers & Nadeau, 2005), with a mathematical formalization of Huey & Slatkin’s (1976) cost–benefit model that indicated that thermoregulatory effort is predicted to increase under certain conditions when thermal quality decreases (Alford & Lutterschmidt, 2018), with an extension of Huey & Slatkin’s (1976) cost–benefit model to include high temperatures that also predicted that thermoregulatory effort should increase when thermal quality decreases (Vickers et al ., 2011), and with experimental manipulations of thermal quality (Basson et al ., 2016). The explanation Blouin‐Demers & Nadeau (2005) proposed was that the physiological disadvantages of thermoconformity are small in thermally benign habitats (high thermal quality) because T b is close to T o even in the absence of thermoregulatory behaviour in such habitats.…”
Section: Discussionsupporting
confidence: 86%
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“…During the day, lizards were more effective thermoregulators where thermal quality was lower (high elevation). These results are consistent with those of a global analysis of the effect of thermal quality on thermoregulation of lizards that indicated that poor thermal quality led to higher effectiveness of thermoregulation (Blouin‐Demers & Nadeau, 2005), with a mathematical formalization of Huey & Slatkin’s (1976) cost–benefit model that indicated that thermoregulatory effort is predicted to increase under certain conditions when thermal quality decreases (Alford & Lutterschmidt, 2018), with an extension of Huey & Slatkin’s (1976) cost–benefit model to include high temperatures that also predicted that thermoregulatory effort should increase when thermal quality decreases (Vickers et al ., 2011), and with experimental manipulations of thermal quality (Basson et al ., 2016). The explanation Blouin‐Demers & Nadeau (2005) proposed was that the physiological disadvantages of thermoconformity are small in thermally benign habitats (high thermal quality) because T b is close to T o even in the absence of thermoregulatory behaviour in such habitats.…”
Section: Discussionsupporting
confidence: 86%
“…Blouin‐Demers & Nadeau, 2005) and theoretical advances (e.g. Vickers et al ., 2011; Alford & Lutterschmidt, 2018). Across an elevational gradient where the costs of thermoregulation become higher with increasing elevation, it appears that the disadvantages associated with thermoconformity when thermal quality is low are more important in influencing investment into thermoregulation than the costs incurred for thermoregulation by S .…”
Section: Discussionmentioning
confidence: 99%
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“…Differences in water fluxes between sexes and age-classes can thus hardly explain the here observed patterns, while differences in thermoregulatory activity are congruent with the observed effects. If precipitation is falling, common lizards hide and are thus not able to thermoregulate, and differences in thermoregulation directly feed back into growth and timing of egg laying 29 . Moreover, thermoregulatory capacity is known to depend on body size 28 and on coloration 30 .…”
Section: Discussionmentioning
confidence: 99%
“…Carryover effects, impacts of events in one season that are realized in a later season (O'Connor et al, 2014), could also delay the appearance of tolerance costs. Additionally, extensions of the cost–benefit framework we used have asserted that while the original model (Huey & Slatkin, 1976) quantified costs of tolerance in energetic terms, these units overlook broader fitness costs (e.g., predation risk, infection, and fecundity) that may be even more critical, especially at warm temperatures (Alford & Lutterschmidt, 2018; Vickers et al, 2011). For example, though body size distributions of our focal groups before dam construction are unknown, the stark difference in FL we observed could reflect a fitness cost of physiological tolerance in Keno trout.…”
Section: Discussionmentioning
confidence: 99%