| Literature DB >> 34188806 |
David J Mitchell1,2, Christa Beckmann1,3,4, Peter A Biro1.
Abstract
Behavioral and physiological ecologists have long been interested in explaining the causes and consequences of trait variation, with a focus on individual differences in mean values. However, the majority of phenotypic variation typically occurs within individuals, rather than among individuals (as indicated by average repeatability being less than 0.5). Recent studies have further shown that individuals can also differ in the magnitude of variation that is unexplained by individual variation or environmental factors (i.e., residual variation). The significance of residual variation, or why individuals differ, is largely unexplained, but is important from evolutionary, methodological, and statistical perspectives. Here, we broadly reviewed literature on individual variation in behavior and physiology, and located 39 datasets with sufficient repeated measures to evaluate individual differences in residual variance. We then analyzed these datasets using methods that permit direct comparisons of parameters across studies. This revealed substantial and widespread individual differences in residual variance. The magnitude of individual variation appeared larger in behavioral traits than in physiological traits, and heterogeneity was greater in more controlled situations. We discuss potential ecological and evolutionary implications of individual differences in residual variance and suggest productive future research directions.Entities:
Keywords: animal personality; behavioral plasticity; behavioral predictability; behavioral reaction norm; intraindividual variability
Year: 2021 PMID: 34188806 PMCID: PMC8216950 DOI: 10.1002/ece3.7603
Source DB: PubMed Journal: Ecol Evol ISSN: 2045-7758 Impact factor: 2.912
FIGURE 1Displayed are the individual best estimates with one standard deviation of the credible distribution in bold and the 95% credible distributions shown by the thin lines. Different traits are assorted by color, and meta‐analytical models of model 3 are presented in panel b. Numbers above each estimate correspond to the study identity. 1: Western fence lizard (Sceloporus occidentalis; Adolph & Pickering, 2008), 2: chacma baboon (Papio ursinus; Allan et al., 2020), 3: mosquitofish (Gambusia holbrooki; Biro & Adriaenssens, 2013), 4: Ward's damselfish (Pomacentrus bankanensis; Biro et al., 2010), 5: guppy (Poecilia reticulata; Biro et al., 2016), 6: hermit crab (Pagurus bernhardus; Bridger et al., 2015), 7: hermit crab (P. bernhardus; Briffa, 2013), 8: hermit crab (P. bernhardus; Briffa et al., 2013), 9: house sparrow (Passer domesticus; Careau, Hoye, et al., 2014), 10: marsh periwinkle (Littoraria irrorata; Cornwell et al., 2018), 11: marsh periwinkle (L. irrorata; Cornwell et al., 2020), 12: house mouse (Mus musculus; Eisenmann et al., 2009), 13: three‐spined stickleback (Gasterosteus aculeatus; Fürtbauer et al., 2015), 14: shore crab (Carcinus maenas; Fürtbauer, 2015), 15: dog (Canis familiaris; Goold & Newberry, 2017), 16: guppy (P. reticulata; Herczeg et al., 2019), 17: brown bear (Ursus arctos; Hertel, Royauté, et al., 2020), 18: African elephant (Loxodonta africanus; Hertel, Niemelä, et al., 2020), 19: Namibian rock agama (Agama planiceps; Highcock & Carter, 2014), 20: slater (Armadillidium vulgare; Horváth et al., 2019), 21: fallow deer (Dama dama; Jennings et al., 2013), 22: three‐spined stickleback (G. aculeatus; Jolles et al., 2019), 23: guppy (P. reticulata; Kurvers et al., 2018), 24: yellow‐bellied marmot (Marmota flaviventris; Martin et al., 2017), 25: guppy (P. reticulata; Mitchell et al., 2016), 26: zebra fish (Danio rerio; Mitchell, Dujon, et al., 2020), 27: guppy (P. reticulata; Mitchell, Beckmann, et al., 2020), 28: guppy (P. reticulata; Mitchell, Lefèvre, et al., 2020), 29: eastern chipmunk (Tamias striatus; Montiglio et al., 2015), 30: hermit crab (P. bernhardus; Nanninga et al., 2020), 31: (Norin & Gamperl, 2017), 32: zebra fish (D. rerio; O'Dea et al., 2020), 33: (Osborn & Briffa, 2017), 34: guppy (P. reticulata; Prentice et al., 2020), 35: hermin crab (P. bernhardus; Stamps et al., 2012), 36: agile frog tadpole (Rana dalmatina; Urszán Tamás et al., 2018), 37: hermit crab (P. bernhardus; Velasque & Briffa, 2016), 38: red‐winged blackbird (Agelaius phoeniceus; Westneat et al., 2013), 39: pied flycatcher (Ficedula hypoleuca; Westneat et al., 2017
IGURE 2FShown are simulated data to illustrate what individual variation in rIIV looks like, under different effect sizes of CVP. Thirty Individuals are simulated, each with 20 observations. Individuals are then ranked from smallest to largest variance, and simulated data points are shown as a residual deviance from 0. When sample sizes are reduced, the heterogeneity appears greater, especially at the null (a). Code to replicate these simulations can be found in the Appendix S1