Effects of climate change on phenology, frost damage, and floral abundance of montane wildflowers.

By David I. Inouye. Ecology, 2008

1,063 citations recorded by the source corpus.

Subfields: Ecological Modeling, Nature and Landscape Conservation, Plant Science

View Paper: https://www.semanticscholar.org/paper/d0e9815b8992a89d37c69efbc4d1ef93d28e62f5

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Citations in the corpus

Why does phenology drive species distribution? (2010, background): “On the contrary, the perennial herbaceous mountain species Delphinium barbeyi, Erigeron speciosus and Helianthella quinquenervis show a lower reproductive success when flowering earlier (Inouye 2008).”
Biodiversity, phenology and temporal niche differences between native- and novel exotic-dominated grasslands (2011, background): “…are attempting to estimate whether spring greenup and other phenological changes are occurring in response to global climate change (Betancourt et al., 2005; Cleland et al., 2007; Rich et al., 2008; Inouye, 2008; Miller-Rushing and Primack, 2008; Miranda et al., 2009; Morisette et al., 2009).”
Advances in flowering phenology across the Northern Hemisphere are explained by functional traits (2018, background): “Flowering season: month of first/ last flowering Early-flowering species are vulnerable to late frost events (Inouye, 2008), whereas late-flowering species may be more vulnerable to summer droughts (Franks, 2011; Wu, Lowry, Nutter, & Willis, 2010).”
The effect of repeated, lethal sampling on wild bee abundance and diversity (2015, background): “Likewise, extreme drought and freezing events (Inouye 2008) in 2012 resulted in extremely low floral resources during that summer, which may have caused the near absence of Bombus spp. workers.”
Ecological effects of extreme drought on Californian herbaceous plant communities (2016, background): “S3) likely produced a sharply diminished growing- season water supply and may possibly also have caused freezing damage (Inouye 2008).”
Response of individual components of reproductive phenology to growing season length in a monocarpic herb (2011, background): “The compressed reproductive schedule may also alter biotic interactions such as with pollinators or herbivores (Elzinga et al. 2007; Hegland et al. 2009) or other abiotic factors (Giménez-Benavides, Escudero& Iriondo 2007; Inouye 2008; Jentsch et al. 2009), thereby reducing fecundity.”
Intraseasonal climate and habitat‐specific variability controls the flowering phenology of high alpine plant species (2010, background): “Strong effects of photoperiod, which protects plants from starting too early and subsequently suffering from frost damage (Inouye 2000, 2008), can be expected for plants in exposed habitats, while the timing of snowmelt should be the key factor for plant development in snowbeds.”
Why Climate Change Makes Riparian Restoration More Important than Ever: Recommendations for Practice and Research (2009, neutral): “How will the phenology of riparian plants and animals respond to climate change? Another ecological challenge of climate change is the loss of synchrony between reproductive phenology and resource availability or natural disturbances (Both and Visser 2001, Inouye 2008 ).”
The effects of phenological mismatches on demography (2010, background): “For example, in Colorado, some plant species are initiating growth earlier in the spring, exposing flower buds to frosts; consequently, seed production has declined dramatically for some species (Inouye 2008).”
Plant–pollinator interactions and phenological change: what can we learn about climate impacts from experiments and observations? (2015, background): “Early snowmelt increases the risk that late-spring frosts will damage the fl ower buds of certain plants (Inouye 2008); this, too, reduces seed production and availability of fl oral resources (Boggs and Inouye 2012; as mentioned above).”
Berry production drives bottom – up effects on body mass and reproductive success in an omnivore (2018, background): “Next to changes in plant productivity (Post and Stenseth 1999) and a longer growing season (Inouye 2008), plant responses to a warming climate also include a shift in the timing of fruit ripening (Menzel et al.”
How does climate warming affect plant-pollinator interactions? (2009, background): “On the other hand, observational studies have shown that increasing spring temperatures may decrease flower abundance (Inouye et al. 2003) and affect species abundance in contrasting ways within a community (Tyler 2001).”
Phenology, growth, and fecundity of eight subarctic tundra species in response to snowmelt manipulations (2010, background): “This 1 year experiment is not able to prove that these patterns hold true for other years or different species, however, a relationship between snowmelt, phenology, and temporal niche has also been found (although not always explicitly stated) in several other snow manipulation studies (Galen and St”
Interactive effects of anthropogenic nitrogen enrichment and climate change on terrestrial and aquatic biodiversity (2013, background): “Earlier snowmelt associated with elevated temperatures has been shown to harm some species of wildflowers through increased frost damage (Inouye 2008).”
Integrating ensemble species distribution modelling and statistical phylogeography to inform projections of climate change impacts on species distributions (2013, background): “Reduced snowpack in spring resulted in increased exposure of leaf and flower buds to early spring frost events, reducing seed production and impacting demographic recruitment (Inouye 2008).”