Hannah E. Marx’s research while affiliated with University of New Mexico and other places

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Publications (3)


Change in relative abundance of invaders over the course of the experiment.
Partial effects plots depicting the effects of each predictor on summed invader biomass: (a–c) Solidago altissima biomass, (d, e) non‐native invader biomass, (f) total invader biomass. For statistical models, biomass data were log‐transformed and predictors were scaled and centred; however, plots show the raw values for ease of interpretation. The solid line represents the mean invader biomass predicted by the model and the ribbons represent 95% confidence intervals.
Partial effect plots showing the relationship of each predictor with biomass of individual invaders: (a) non‐native invader species, (b, c) native invader species, (d, e) biomass of all invader species. The solid line represents the mean predicted change in invader biomass over time while the ribbons represent the 95% confidence intervals.
Partial effects plots depicting the effect of phylogenetic diversity on invader biomass over time. The solid line represents the mean predicted change in invader biomass over time while the ribbons represent the 95% confidence intervals.
Dominant species establishment may influence invasion resistance more than phylogenetic or functional diversity
  • Article
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November 2023

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194 Reads

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7 Citations

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Phylogenetic and functional diversity are theorised to increase invasion resistance. Experimentally testing whether plant communities higher in these components of diversity are less invasible is an important step for guiding restoration designs. To investigate how phylogenetic and functional diversity of vegetation affect invasion resistance in a restoration setting, we used experimental prairie restoration plots. The experiment crossed three levels of phylogenetic diversity with two levels of functional diversity while species richness was held constant. We allowed invaders to colonise plots; these included native species from neighbouring plots and non‐native invasive species from a surrounding old field. We tested if invader biomass was influenced by phylogenetic and functional diversity, and phylogenetic and hierarchical trait distances between invaders and planted species. We binned each invader into three categories: native species from neighbouring experimental plots (site‐specific invaders), native species not part of the experimental species pool (native invaders) or non‐native species (non‐native invaders). Counter to expectation, both non‐native and native invaders became more abundant in more phylogenetically diverse plots. However, plots with higher abundance of planted Asteraceae, a dominant family of the tallgrass prairie, had lower invader biomass for both native and non‐native invaders. We also found that hierarchical trait differences shaped invasion. The species that became most abundant were non‐native invaders that were taller, and native invaders with low specific leaf area relative to planted species. Site‐specific invaders were not influenced by any plot‐level diversity metrics tested. Synthesis and application: Our results suggest that greater phylogenetic diversity may lower resistance to invasion. This effect may be due to more even but sparser niche packing in high‐diversity plots, associated with greater availability of unsaturated niche space for colonisation. However, trait composition fostered invasion resistance in two ways in our study. First, establishment of native species with strongly dominant traits may confer invasion resistance. Second, species mixes that optimise trait differences between planted vegetation and likely invaders may enhance invasion‐resistance.

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Partial effects of all native community predictors included in the final pooled model of invasive species abundance (per cent cover). Each plot represents the predicted partial effect of the predictor when all other predictors are held constant. The lines and ribbons indicate the mean and 95% confidence intervals predicted by a generalized linear mixed effects model respectively
Relationship between native phylogenetic diversity and invasive species cover. Values to the left of the red dashed line indicate native communities with lower MPD than expected by chance (phylogenetically clustered), while values to the right indicate native communities with higher than expected MPD (phylogenetically overdispersed). The black line and grey ribbon indicate the mean and 95% confidence intervals predicted by a generalized linear mixed effects model respectively
Relationship between change in native community attributes and invasive species abundance. These three attributes of the native community, native species richness (a), phylogenetic diversity (b) and height MAD (c), demonstrate high variability in uninvaded plots. Green dots indicate plots that were uninvaded and remained uninvaded throughout all surveys. Purple dots indicate plots that had become invaded. The y‐axis indicates the observed change in each native community attribute at each plot over the surveys
The invasion paradox dissolves when using phylogenetic and temporal perspectives

November 2021

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229 Reads

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26 Citations

The prediction that higher biodiversity leads to denser niche packing and thus higher community resistance to invasion has long been studied, with species richness as the predominant measure of diversity. However, few studies have explored how phylogenetic and functional diversity, which should represent niche space more faithfully than taxonomic diversity, influence community invasibility, especially across longer time frames and over larger spatial extents. We used a 15‐year, 150‐site grassland dataset to assess relationships between invasive plant abundance and phylogenetic, functional and taxonomic diversity of recipient native plant communities. We analysed the dataset both pooled across all surveys and longitudinally, leveraging time‐series data to compare observed patterns in invasion with those predicted by two community assembly processes: biotic resistance and competitive exclusion. We expected more phylogenetically and functionally diverse communities to exhibit greater resistance to invasion. With the pooled dataset, we found support for the long‐standing observation that communities with more native species have lower abundance of invasive species, and a more novel finding that more phylogenetically diverse communities had higher abundance of invasive species. We found no influence of aggregate (multivariate) functional diversity on invasion, but assemblages with taller plants, lower variability in plant height and lower seed mass were less invaded. Viewed longitudinally, the phylogenetic diversity relationship was reversed: the most phylogenetically diverse communities were most resistant to invasion. This apparent discrepancy suggests invasion dynamics are influenced by both site attributes and biotic resistance and emphasizes the value in studying invasion across time. Synthesis. Our results provide insight into the nuances of the diversity–invasibility relationship: invasion dynamics differed for different dimensions of diversity and depending on whether the relationship was evaluated longitudinally. Our findings highlight the limitations of using single time‐point ‘snapshots’ of community composition to infer invasion mechanisms.


Phylogenetic relationships of entomophilous flowering plants observed on Galiano Island, with labels showing provenance and life history of species
Mean soil moisture across each site class from April through August, shown with 95% confidence intervals (LMM estimates). Soil moisture was estimated as volumetric water content (%VWC), a ratio of water to soil (m³/m³), using a TDR probe. All differences in wet versus dry site conditions are significant at p = <.001–.001
(a) Model outputs of counts of flowering shoots across habitats and samples, with 95% confidence intervals. Significant differences between site conditions, both for independent samples and across sample ranges, are marked with letters (a is significantly different from b, x significantly different than y). All differences significant at p = <.001–.02. (b) Model outputs of counts of flowering shoots among native versus exotic plants across habitats and samples, with 95% confidence intervals. Asterisks indicate significant differences between native versus exotic FRA at * (p < .05) and *** (p < .001). ⁂ indicates that significance could not be calculated because only exotic species are present. (c) Standardized effect size of Mean Pairwise Distance (MPD z) calculated for native and exotic plant assemblages across site conditions and samples at the community level; negative values indicate increasingly clustered plant assemblages. Significance indicated at * (p < .05), and ** (p < .01). A bullet (•) marks a near‐significant clustering event (p = .056)
Standardized effect size of the phylogenetic metric mean nearest taxon distance (MNTD z), calculated for transects, regressed against log‐transformed soil volumetric water content (logVWC)
Phylogenetic restriction of plant invasion in drought‐stressed environments: Implications for insect‐pollinated plant communities in water‐limited ecosystems

July 2021

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74 Reads

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9 Citations

Background Plant–pollinator community diversity has been found to decrease under conditions of drought stress; however, research into the temporal dimensions of this phenomenon remains limited. In this study, we investigated the effect of seasonal drought on the temporal niche dynamics of entomophilous flowering plants in a water-limited ecosystem. We hypothesized that closely related native and exotic plants would tend to share similar life history and that peak flowering events would therefore coincide with phylogenetic clustering in plant communities based on expected phenological responses of plant functional types to limitations in soil moisture availability. Location Galiano Island, British Columbia, Canada. Methods Combining methods from pollinator research and phylogenetic community ecology, we tested the influence of environmental filtering over plant community phenology across gradients of landscape disturbance and soil moisture. Floral resource availability and community structure were quantified by counts of flowering shoots. We constructed a robust phylogeny to analyze spatial and temporal variation in phylogenetic patterns across the landscape, testing the significance of the observed patterns against a randomly generated community phylogeny. Phylogenetic metrics were then regressed against factors of disturbance and soil moisture availability. Results Critical seasonal fluctuations in floral resources coincided with significant phylogenetic clustering in plant communities, with decreasing plant diversity observed under conditions of increasing drought stress. Exotic plant species in the Asteraceae became increasingly pervasive across the landscape, occupying a late season temporal niche in drought-stressed environments. Main conclusion Results suggest that environmental filtering is the dominant assembly process structuring the temporal niche of plant communities in this water-limited ecosystem. Based on these results, and trends seen elsewhere, the overall diversity of plant–pollinator communities may be expected to decline with the increasing drought stress predicted under future climate scenarios.

Citations (3)


... A common recommendation is to plant native plants with this same strategy because plants with conservative traits will be unlikely to compete with invasive plants employing an acquisitive strategy (Laughlin 2014;Yannelli et al. 2018). However, there has been some evidence to the contrary in grassland ecosystems (Catford et al. 2019;Ernst et al. 2023). Few studies have investigated the degree to which diversity, niche-based processes, and ecological strategy shape the invasion process. ...

Reference:

Diverse Ecological Strategies Increase Invasion Resistance in an Experimental Grassland Restoration
Dominant species establishment may influence invasion resistance more than phylogenetic or functional diversity

... These conditions favor fast growth and reproduction rates. Our study and others that have found more conservative traits to be more competitive against invaders have taken place in lower resource environments with a disturbance regime that aims to approximate historical patterns (Catford et al. 2019;Ernst et al. 2022). ...

The invasion paradox dissolves when using phylogenetic and temporal perspectives

... In this region, protein resources (pollen) are scarce during certain periods of the year, particularly during the rainy season [13]. Rainfall, temperature, and soil type can lead to drought periods affecting plant phenology, limiting the diversity and availability of nectar and pollen-producing flora [14]. It causes the formation of a small abdomen, which affects the development of the organs inside, including, among them, the size of the testicles and seminal vesicles [15]. ...

Phylogenetic restriction of plant invasion in drought‐stressed environments: Implications for insect‐pollinated plant communities in water‐limited ecosystems