2017
DOI: 10.1111/gcb.13666
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Phenotypic distribution models corroborate species distribution models: A shift in the role and prevalence of a dominant prairie grass in response to climate change

Abstract: Phenotypic distribution within species can vary widely across environmental gradients but forecasts of species' responses to environmental change often assume species respond homogenously across their ranges. We compared predictions from species and phenotype distribution models under future climate scenarios for Andropogon gerardii, a widely distributed, dominant grass found throughout the central United States. Phenotype data on aboveground biomass, height, leaf width, and chlorophyll content were obtained f… Show more

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Cited by 39 publications
(46 citation statements)
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References 53 publications
(120 reference statements)
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“…, Smith et al. ). Seedlings generally produced more biomass and needles with warming, and root‐to‐shoot length ratios increased, with Douglas‐fir increasing more than lodgepole pine.…”
Section: Discussionmentioning
confidence: 99%
“…, Smith et al. ). Seedlings generally produced more biomass and needles with warming, and root‐to‐shoot length ratios increased, with Douglas‐fir increasing more than lodgepole pine.…”
Section: Discussionmentioning
confidence: 99%
“…This variation can dramatically modify inferences about behavioural patterns and fitness (Adolph & Porter, ) and, therefore, estimations of climate impacts accounting for trait (Cochrane, Yates, et al., ) or niche (Pearman, D'Amen, Graham, Thuiller, & Zimmermann, ) variation within species. For instance, phenotypic and species distributions can track different aspects of climate change (e.g., temperature vs. precipitation) and both complement impact assessments (Smith et al., ), climate effects can be masked by thermoregulation interacting with topography (Sears et al., ) and spatial scale (Barton, Clusella‐Trullas, & Terblanche, ), latitudinal enhancement of heat tolerance might signal recent poleward range expansions (Lancaster, ), while species distribution models can fail to detect constrains in population expansion (Kolbe et al., ) or area of occupancy (Benito Garzón et al., ) owing to trait plasticity. To illustrate this point, we predicted annual restriction times of 596, 668, 697 and 715 hr per 5 × 5 km 2 grid cell using the CT max of each of four populations of the Schreiber's green lizard L. schreiberi (CT max range = 40.5–42.9°C across individuals, and 41.0–42.1°C among population medians).…”
Section: Discussionmentioning
confidence: 99%
“…This variation can dramatically modify inferences about behavioural patterns and fitness (Adolph & Porter, 1993) and, therefore, estimations of climate impacts accounting for trait or niche (Pearman, D'Amen, Graham, Thuiller, & Zimmermann, 2010) variation within species. For instance, phenotypic and species distributions can track different aspects of climate change (e.g., temperature vs. precipitation) and both complement impact assessments (Smith et al, 2017), climate effects can be masked by thermoregulation interacting with topography (Sears et al, 2011) and spatial scale (Barton, Clusella-Trullas, & Terblanche, 2018), latitudinal enhancement of heat tolerance might signal recent poleward range expansions (Lancaster, 2016), while species distribution models can fail to detect constrains in population expansion (Kolbe et al, 2010) where it is mostly restricted to riparian shrubs in mountain ranges and low temperate forests close to mountain slopes (Monasterio, Shoo, Salvador, Iraeta, & Díaz, 2013). Our population-based modelling variation above would imply differences in predicted annual restriction times for the species from 85 to 102 seven-hour days per grid cell during which individuals would be forced to shelter from overheating.…”
Section: Discussionmentioning
confidence: 99%
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“…nuclear microsatellites). Likewise, a better understanding of how functional traits relate to the environment (Kostikova et al 2013, Soudzilovskaia et al 2013, Smith et al 2017) coupled with growing databases on traits (Kattge et al 2011) could help constrain models of species' spread (Angert et al 2011). Additionally, microsatellites, large SNP datasets such as produced by RADseq, and sequences (from nuclear genomes and from chloroplasts) each offer different information content due to mutation and recombination, thus combining marker types should increase the ability of integrative modeling to make demographic inference, a point which to our knowledge is rarely exploited in the literature.…”
Section: Section 4 Continued Challenges and Frontiersmentioning
confidence: 99%