Lockdown still, but collaborators at local site that manage research reserve kindly agreed to collect native seeds.
I just returned from some exciting desert fieldwork! Last year, I sampled the annual plant community under shrubs and in the open at six sites across the Mojave and San Joaquin Deserts, and here’s the gist of what I found:
Spatial association with native foundation shrubs strongly and consistently increased the abundance, biomass, cover, and fitness of the dominant invader Bromus rubens but not the native annual community. This is interesting because positive interactions mediated by native species are seldom invoked to explain the success of exotic invaders. Very cool, but what about the system’s many other exotic, invasive species? Is facilitated invasion species-specific?
To tackle this question, I returned to the desert and sampled the annual plant community at nine study sites scattered across the Mojave and San Joaquin Deserts. Six are repeats from last year, three (Yuc, Cna, Hea) are new:
At each site, I sampled the annual plant community at 20 pairs of shrub and open microsites with a 0.5m x 0.5m quadrat. Shrub microsites were the area immediately beneath the canopies of foundation shrubs, and open microsites were areas >1m from any shrub canopy. In each microsite, I estimated the abundance of the native annual community as a whole and the exotic annual community as a whole. I collected species-specific measurements for the abundance, biomass, and fitness of the following exotic plant species: Bromus rubens, B. tectorum, B. diandrus, Erodium cicutarium, Schismus spp., and Brassica tournefortii. Each of these exotic invaders can contribute to biodiversity loss and diminished ecosystem function.
We’ll have to wait for the official stats, but it seemed that B. rubens, B. tectorum, and B. diandrus formed strong and consistent positive associations with native shrubs. Each of the other exotic species ( E. cicutarium, Schismus spp., and B. tournefortii ) associated with native shrubs more sporadically. The most interesting observation was this: it seemed that B. rubens controlled the game — when it was super abundant under shrubs, nothing else (except other bromes) strongly associated with shrubs. When it was less abundant, other exotic (and sometimes native!) species apparently associated with shrubs more strongly. This suggests a competitive hierarchy in which exotic bromes, and especially B. rubens, rule the understory, followed by other exotic species, followed by native species. Again, the stats will give us the official story, but I think that’s what I saw! Very cool.
More cool stuff:
A progress report by Stephanie Haas
Shrubs frequently have positive interactions with annuals in desert ecosystems. This facilitative effect has been seen repeatedly with plant density, but the effect of shrubs on flowering is less studied. Shrubs also impact other species that interact with annuals, including both herbivores and pollinators. These direct and indirect interactions exist in a complex network that we attempt to tease apart through both manipulation and observation.
To see the slide deck click here.
To see the presentation click here.
Positive interactions are key to many systems worldwide. Foundation species such as shrubs are able to benefit other taxa through various mechanistic pathways. The canopy of these species is also an structural agent, able to reduce light intensity and temperature variation experienced by vertebrates. But, do the instances of animal near a shrub increase as temperature and light intensity increase? Can artificial shelters be as good as shrubs when comes to lowering the variation in the above parameters? Disturbances such as land use and climate change are the current reality of many regions. To be able to artificially restore these systems post-disturbance while new vegetation is grown is thus key.
Click here to find out more!
By: Mario Zuliani
Positive interactions between plant and animal species have been reported in most ecosystems globally. Most literature that looks at these interactions, particularly in arid ecosystems, reports the facilitative interactions occurring between shrub and animal species. With these types of interactions being present, one begs to question; does the density of these foundational shrub species have a relationship with the animal abundance present near them? That being said, understanding this relationship could potentially be used for remediation efforts, for many of the animal species using these shrubs.
For access to my March 2020 Progress report presentation click here
For access to the slide show click here
Malory Owen’s Second-year Masters Progress report
March 19th, 2020
Malory Owen & Christopher Lortie
Positive interactions between plants and animals create habitat infrastructure on which many species rely, especially when the promotion of foundation species is involved. Mutualistic interactions between plants and birds (like pollination or seed dispersal) are dependent on both plant and bird phenology or cyclic/seasonal changes. However, phenology is plastic as photoperiod and temperature largely determine flowering & fruiting for plants and migration & breeding for birds. As our climate changes and habitats degrade, we must understand what interactions are at risk. That’s why, in this study, we examined the relationships between birds, their community, their behavior, and their microhabitat associations.
As a team, we are discussing the fine-scale grain of sampling for estimating annual-annual plant interactions in deserts. We are particularly interested in the Mojave Desert to examine pollinator-herbivore interactions with annuals that are mediated by the other immediately adjacent congeneric species. Here is a brief compilation of key papers examining this challenge.
Publications describing the fine-scale annual plant neighbourhood concept
Mack, R. N. and Harper, J. L. 1977. Interference in dune annuals: spatial pattern and neighbourhood effects. – Journal of Ecology 65: 345-363.
Holzapfel, C. and Mahall, B. E. 1999. Bidirectional facilitation and interference between shrubs and annuals in the Mojave desert. – Ecology 80: 1747-1761.
Schiffers, K. and Tielbörger, K. 2006. Ontogenetic Shifts in Interactions among Annual Plants. – Journal of Ecology 94: 336-341.
Lortie, C. J. and Turkington, R. 2008. Species-specific positive effects in an annual plant community. – Oikos 117: 1511-1521.
Emery, N. C., Stanton, M. L. and Rice, K. J. 2009. Factors driving distribution limits in an annual plant community. – New Phytologist 181: 734-747.
Luzuriaga, A. L., Sánchez, A. M., Maestre, F. T. and Escudero, A. 2012. Assemblage of a Semi-Arid Annual Plant Community: Abiotic and Biotic Filters Act Hierarchically. – PLOS ONE 7: e41270.
Underwood, N., Inouye, B. D. and Hambäck, P. A. 2014. A Conceptual Framework for Associational Effects: When Do Neighbors Matter and How Would We Know? – The Quarterly Review of Biology 89: 1-19.
Underwood, N., Hambäck, P. A. and Inouye, B. D. 2020. Pollinators, Herbivores, and Plant Neighborhood Effects. – The Quarterly Review of Biology 95: 37-57.
I am a fan of the 15cm scale for fine-scale but often sample with a 15cm ring nested within a second 30cm metal ring. I construct using wire.
Here’s my [approximate] travel schedule for this summer. It’d be great to connect any time we happen to be in the same place at the same time!
- April 6-20: Veg sampling and experimental site selection in Cali/Nevada
- May 20(ish): B. rubens seed collection in Cali/Nevada
- May 25-June 2: E. lobata sampling in Toronto
- August 2-7: ESA in Salt Lake
- Sept 16-21: E. lobata sampling in Toronto
- Sept. 25-Oct. 11: Install facilitation x granivory experiment in Cali/Nevada.
One of the most powerful approaches for understanding biological invasions by non-native species is to examine ecological patterns and processes in both the native and non-native ranges of invasive species. Here’s a great article on the subject:
The number of articles published on biological invasions has increased exponentially over the last 20 years, but biogeographically explicit studies replicated in the native and non-native ranges of invasive species are still VERY rare. This hampers our mechanistic understanding of the invasion process and therefore our ability to explain, predict, and manage biological invasions.
Bromus rubens (i.e., red brome) invasion in the Mojave Desert provides a great opportunity to address this knowledge gap. We are planning to examine the individual and joint effects of shrub facilitation and post-dispersal seed predation on the abundance of B. rubens in its native (Israel) and non-native (California and Nevada) ranges. This experiment is broadly interesting because it allows us to test the relative importance of the effects of two fundamental biotic interactions on two continents. Here’s a cartoon of our experimental design:
Solid circles represent functional exclosures that effectively exclude seed predators; dashed circles represent non-functional exclosures that admit seed predators. Note the control treatment that monitors recruitment from seed banks. This is a full-factorial design that crosses shrub facilitation (open vs. shrub microsites) with seed predation (functional vs. non-functional exclosures). Pretty cool.
We will replicate this setup at 5 shrub-open pairs per site at 6 sites across the Mojave (GPS coordinates are preliminary):
We will replicate the experiment at 5 sites in the Negev Desert of Israel with the help of Dr. Merav Seifan of the Ben Gurion University of the Negev. She rocks! Site locations and GPS coordinates in Israel are forthcoming.
The biogeographic contrast of the effects of seed predation can be considered a test of the enemy release hypothesis, which has only been examined once in the context of seed predation:
However, the biogeographic contrast of the effects of shrub facilitation is COMPLETELY NOVEL…I think 🙂
We begin work this spring! We’ll keep you posted.
Panoche Hills Ecological Reserve
Active restoration of native vegetation and seeds.
Contrast with regional patterns of diversity.