8 research outputs found
Root traits vary as much as leaf traits and have consistent phenotypic plasticity among 14 populations of a globally widespread herb
Our understanding of plant functional trait variation among populations and how this relates to local adaptation to environmental conditions is largely shaped by above-ground traits. However, we might expect below-ground traits linked to resource acquisition and conservation to vary among populations that experience different environmental conditions. Alternatively, below-ground traits might be highly plastic in response to growing conditions, such as availability of soil resources and association with symbiont arbuscular mycorrhizal fungi (AMF). We assessed (i) the strength of among-population variation in above- and below-ground traits, (ii) the effects of growing conditions on among-population variation and (iii) whether variation among populations is linked to source environment conditions, in a globally distributed perennial Plantago lanceolata. Using seeds from 14 populations across three continents, we grew plants in a common garden experiment and measured leaf and root traits linked to resource acquisition and water conservation. We included two sets of experimental treatments (high or low water availability; with and without AMF inoculation), which enabled us to assess trait responses to growing conditions. Across treatments, the percentage of root trait variation explained by populations and continents was 9%–26%, compared to 7%–20% for leaf trait variation. From principal component analysis (PCA), the first PC axis for both root and leaf traits largely reflected plant size, while the second PC broadly captured mass allocation. Root mass allocation (PC 2) was related to mean annual temperature and mean moisture index, indicating that populations from cooler, wetter environments had longer, thinner roots. However, we found little support for a relationship between source environment and leaf trait PCs, root system size (PC1) or individual traits. Water availability and AMF inoculation effects on size were consistent among populations, with larger plants under AMF inoculation, and less mass allocation to leaves under lower water availability. Plantago lanceolata shows substantial population-level variation in a suite of root traits, but that variation is only partially linked to the source environmental variables studied. Despite considerable differences in source abiotic environments, geographically separated populations have retained a strong and similar capacity for phenotypic plasticity both above and below-ground. Read the free Plain Language Summary for this article on the Journal blog.</p
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Predicting invasion in grassland ecosystems: is exotic dominance the real embarrassment of richness?
Invasions have increased the size of regional species pools, but are typically assumed to reduce native diversity. However, global-scale tests of this assumption have been elusive because of the focus on exotic species richness, rather than relative abundance. This is problematic because low invader richness can indicate invasion resistance by the native community or, alternatively, dominance by a single exotic species. Here, we used a globally replicated study to quantify relationships between exotic richness and abundance in grass-dominated ecosystems in 13 countries on six continents, ranging from salt marshes to alpine tundra. We tested effects of human land use, native community diversity, herbivore pressure, and nutrient limitation on exotic plant dominance. Despite its widespread use, exotic richness was a poor proxy for exotic dominance at low exotic richness, because sites that contained few exotic species ranged from relatively pristine (low exotic richness and cover) to almost completely exotic-dominated ones (low exotic richness but high exotic cover). Both exotic cover and richness were predicted by native plant diversity (native grass richness) and land use (distance to cultivation). Although climate was important for predicting both exotic cover and richness, climatic factors predicting cover (precipitation variability) differed from those predicting richness (maximum temperature and mean temperature in the wettest quarter). Herbivory and nutrient limitation did not predict exotic richness or cover. Exotic dominance was greatest in areas with low native grass richness at the site- or regional-scale. Although this could reflect native grass displacement, a lack of biotic resistance is a more likely explanation, given that grasses comprise the most aggressive invaders. These findings underscore the need to move beyond richness as a surrogate for the extent of invasion, because this metric confounds monodominance with invasion resistance. Monitoring species’ relative abundance will more rapidly advance our understanding of invasions.This is the publisher’s final pdf. The published article is copyrighted by John Wiley & Sons Ltd and can be found at: http://onlinelibrary.wiley.com/journal/10.1111/(ISSN)1365-2486
Novel insights into post-glacial vegetation change: functional and phylogenetic diversity in pollen records
QuestionHow do pollen-based functional and phylogenetic diversity help to explain post-glacial vegetation change in relation to climate and human influence? LocationEstonia and Latvia, NE Europe. MethodsWe used a data set of 1062 pollen samples from 20 sites covering the last 14500yrs to estimate plant richness, evenness, functional and phylogenetic diversity (community-weighted mean and mean pair-wise distance). We adjusted existing functional and phylogenetic diversity measures for the pollen data and tested the methods with a simulation study. The simulations showed that species-based and pollen-based diversity estimates were all significantly positively correlated. ResultsThe Late Glacial (14500-11650cal. yr BP) and the mid-Holocene (8000-4000cal. yr BP) periods showed contrasting values for most of the diversity components, and several diversity estimates were strongly associated with climate. The cold climate during the Late Glacial led to high phylogenetic diversity, and relatively low functional diversity. Climate warming during the transition from the Late Glacial to the Holocene was followed by a decrease in phylogenetic diversity but an increase in functional diversity based on plant height and seed weight. Increasing human impact in the late Holocene was associated with an increase in plant richness and decreases in functional diversity based on plant height and seed weight and in phylogenetic diversity of herbs. ConclusionsPollen-based functional and phylogenetic diversity provide novel insights into post-glacial vegetation change and its drivers. Both functional and phylogenetic diversity were closely related to climatic conditions, suggesting that trait differences play an important role in long-term community response to climate change. Our results indicate that human impact during the last two millennia has influenced functional and phylogenetic diversity negatively by suppressing plants with certain traits (functional convergence) and giving advantage to plants from certain phylogenetic lineages. We see great potential in the further development of functional and phylogenetic diversity methods for pollen data
Determinants of fine-scale plant diversity in dry calcareous grasslands within the Baltic Sea region
We used an extensive dataset (1220 vegetation plots of 1 m(2)) to study vegetation gradients and fine-scale plant diversity in dry calcareous grasslands (including alvar grasslands) in the Baltic Sea region. The study area covers the entire European distributional range of alvar habitats: Sweden (Oland, Gotland, Gotaland), Estonia (Saaremaa, Hiiumaa, north Estonia, west Estonia), and western Russia (Izhora, lzborsk). Fine-scale plant diversity was characterized by species richness and standardized phylogenetic diversity (comparing the observed mean pairwise phylogenetic distance (MPD) with MPD values from random communities). Ordination techniques (DCA) were used to characterize the main vegetation gradient. Variables describing local environment, climate, the biogeographic composition of the plant communities, and geographic location were related to fine-scale species richness and phylogenetic diversity using variation partitioning techniques and linear mixed models. The main vegetation gradient in the dry calcareous grasslands in the Baltic Sea region had a strong geographic component, was associated with soil depth, species' stress- and disturbance-tolerance and the age of the grassland habitat. Fine-scale phylogenetic diversity and species richness were negatively associated suggesting that these two diversity components are influenced by different sets of environmental and historical parameters. Fine-scale species richness was unimodally associated with the main vegetation gradient, and the highest levels of species richness were found under intermediate environmental (disturbance, light conditions and temperature) conditions where there was a mixture of species from different biogeographic regions. In contrast to species richness, fine-scale phylogenetic diversity was negatively associated with the main vegetation gradient. The highest phylogenetic diversity was found in the extremely thin-soiled alvar grasslands in Gotaland and on the Baltic islands (especially on Oland) where the high phylogenetic diversity is likely to be a reflection of a long history of continuous openness that has allowed time for the "collection" of phylogenetically different species within these unique habitats. (C) 2012 Elsevier B.V. All rights reserved
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LambrinosJohnHorticulturePredictingInvasionGrassland.pdf
Invasions have increased the size of regional species pools, but are typically assumed to reduce native diversity.
However, global-scale tests of this assumption have been elusive because of the focus on exotic species richness,
rather than relative abundance. This is problematic because low invader richness can indicate invasion resistance by
the native community or, alternatively, dominance by a single exotic species. Here, we used a globally replicated
study to quantify relationships between exotic richness and abundance in grass-dominated ecosystems in 13 countries
on six continents, ranging from salt marshes to alpine tundra. We tested effects of human land use, native community
diversity, herbivore pressure, and nutrient limitation on exotic plant dominance. Despite its widespread use,
exotic richness was a poor proxy for exotic dominance at low exotic richness, because sites that contained few exotic
species ranged from relatively pristine (low exotic richness and cover) to almost completely exotic-dominated ones
(low exotic richness but high exotic cover). Both exotic cover and richness were predicted by native plant diversity
(native grass richness) and land use (distance to cultivation). Although climate was important for predicting both
exotic cover and richness, climatic factors predicting cover (precipitation variability) differed from those predicting
richness (maximum temperature and mean temperature in the wettest quarter). Herbivory and nutrient limitation
did not predict exotic richness or cover. Exotic dominance was greatest in areas with low native grass richness at the
site- or regional-scale. Although this could reflect native grass displacement, a lack of biotic resistance is a more likely
explanation, given that grasses comprise the most aggressive invaders. These findings underscore the need to move
beyond richness as a surrogate for the extent of invasion, because this metric confounds monodominance with invasion
resistance. Monitoring species’ relative abundance will more rapidly advance our understanding of invasions
Recommended from our members
LambrinosJohnHorticulturePredictingInvasionGrasslandSupportingInformation.pdf
Invasions have increased the size of regional species pools, but are typically assumed to reduce native diversity.
However, global-scale tests of this assumption have been elusive because of the focus on exotic species richness,
rather than relative abundance. This is problematic because low invader richness can indicate invasion resistance by
the native community or, alternatively, dominance by a single exotic species. Here, we used a globally replicated
study to quantify relationships between exotic richness and abundance in grass-dominated ecosystems in 13 countries
on six continents, ranging from salt marshes to alpine tundra. We tested effects of human land use, native community
diversity, herbivore pressure, and nutrient limitation on exotic plant dominance. Despite its widespread use,
exotic richness was a poor proxy for exotic dominance at low exotic richness, because sites that contained few exotic
species ranged from relatively pristine (low exotic richness and cover) to almost completely exotic-dominated ones
(low exotic richness but high exotic cover). Both exotic cover and richness were predicted by native plant diversity
(native grass richness) and land use (distance to cultivation). Although climate was important for predicting both
exotic cover and richness, climatic factors predicting cover (precipitation variability) differed from those predicting
richness (maximum temperature and mean temperature in the wettest quarter). Herbivory and nutrient limitation
did not predict exotic richness or cover. Exotic dominance was greatest in areas with low native grass richness at the
site- or regional-scale. Although this could reflect native grass displacement, a lack of biotic resistance is a more likely
explanation, given that grasses comprise the most aggressive invaders. These findings underscore the need to move
beyond richness as a surrogate for the extent of invasion, because this metric confounds monodominance with invasion
resistance. Monitoring species’ relative abundance will more rapidly advance our understanding of invasions
TRY plant trait database - enhanced coverage and open access
10.1111/gcb.14904GLOBAL CHANGE BIOLOGY261119-18