Abstract
Long‐term observational studies have detected greening and shrub encroachment in the subarctic attributed to current climate change, while global change simulations have showed that community composition and productivity may shift drastically in arctic, subarctic, and alpine tundra plant communities in the future. However, responses to global change can be highly species‐ and context‐dependent. We examined community‐level and species‐specific responses to a six‐year factorial temperature and nutrient (nitrogen and phosphorus) amendment experiment in two alpine plant communities in northern Sweden: a species‐poor dwarf shrub heath, and a more species‐rich meadow. We hypothesized that abundance responses to global change would be variable within commonly defined vascular plant functional groups (e.g., forbs, evergreen shrubs, deciduous shrubs) and that new species would appear in experimental plots over time due to the ameliorated growing conditions. We found that within most functional groups, species were highly individualistic with respect to the global change simulation, particularly within the forbs, whereas within the shrubs, responses were neutral to negative and widely variable in magnitude. In the heath community the response of the graminoid functional group was driven almost entirely by the grass Calamagrostis lapponica, which increased in abundance by an order of magnitude in the combined temperature and nutrient treatment. Furthermore, community context was important for species' responses to the simulations. Abundance of the pan‐arctic species Carex bigelowii and Vaccinium vitis‐idaea responded primarily to the temperature treatment in the meadow community whereas the nutrient treatment had stronger effects in the heath community. Over six growing seasons, more new species appeared in the experimental plots than in control plots in the meadow community, whereas in the heath community only one new species appeared. Our results from two closely situated but different plant communities show that functional groups do not predict individual species responses to simulated global change, and that these responses depend to a large extent on pre‐existing physical conditions as well as biotic interactions such as competition and facilitation. It may be difficult to apply general trends of global change responses to specific local communities.
Highlights
Global change is already affecting high-latitude and high-altitude ecosystems, responses in the Arctic and subarctic have been highly heterogeneous because of the complexity and diversity of natural systems (IPCC 2014)
For individual species analyzed in the meadow community, one or both of the components of the global change simulation was included in the mixed-effects species cover model with the best fit (Table 1)
Shrubs.—Within the shrub functional group, we found a trend of decreasing cover when nutrients were added in almost every species and across both the heath and meadow sites
Summary
Global change is already affecting high-latitude and high-altitude ecosystems, responses in the Arctic and subarctic have been highly heterogeneous because of the complexity and diversity of natural systems (IPCC 2014). Changes in plant abundance and diversity have important effects across trophic levels, including on insect and mammalian herbivores through changes in forage availability and quality (Post et al 2009). Measuring and predicting these changes in vascular plant communities are challenging. The functional group theory states that vascular plants will show consistent responses to global change within their functional group (Chapin et al 1996), a concept useful to compare between or generalize across many unique ecosystems with varying community composition. The specificity of local ecosystems may limit the utility of the functional group theory, as local biotic and physical conditions may contribute to determining responses to global change (Elmendorf et al 2012)
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