Showing posts with label ESA meeting. Show all posts
Showing posts with label ESA meeting. Show all posts

Friday, July 14, 2017

Making conference talks compelling and meaningful

Langin, K. 2017. “Tell me a story! A plea for more compelling conference presentations”. The Condor 119(2):321-326.

Communicating complex ideas that rely on the accumulation of ideas, methods, and data is undeniably hard. Some people are naturals at presenting their work, but for many of us (definitely for me) it is a skill that only improves with lots of practice. With conference season in full swing, Kathryn Langin’s paper on this very topic is timely. She provides excellent advice, particularly on how to overcome the common pitfalls of “unclear questions, too much text, unreadable figures, no overarching storyline”. In particular, the appendix provides step-by-step advice on crafting talks and composing slides that should help both first timers and more experienced presenters. 


Langin notes that we treat scientists differently from other audiences: “Scientists are increasingly trained to distill research findings for audiences that lack a strong background in science (Baron 2010). However, we often fail to put those strategies to work when communicating with other scientists, which is unfortunate because many scientists lack deep knowledge of topics outside their immediate field (Pickett et al. 1991),” and “If we cannot effectively communicate our research to colleagues, then how are we going to communicate it to resource managers, policy makers, the media, and the general public?”

This is a worthy goal. But it’s also true that there isn’t perfect equivalence between these different types of talks, and while the techniques that make for public talks are useful across the board, they aren’t enough on their own. I’ve seen the odd talk where popular science video clips, overly-processed slides, or lengthy quotations took the place of substantive research, and there’s little I find more frustrating. So, to make Langin’s advice even more difficult, good science communication requires recognizing what information, and particularly what depth of information, must be communicated for a particular audience. For scientist audiences, speakers benefit from being able to make complicated ideas seem straightforward while not insulting the listener or glossing over the difficult.

Conference audiences are difficult because they tend to be a mix of different people with varied reasons for attending a particular talk. They could be specialists who sought your talk out based on the abstract, generalists in the broader area of study, or just scientists sitting randomly in the room waiting for the next talk. And while Langin says, “Science is both increasingly collaborative and increasingly specialized; an ability to communicate beyond scientists in your immediate field is important. While it may be tempting to tailor your presentation for the expert that you hope (or fear) will be in attendance (e.g., by packing it with methodological minutiae and mountains of data), such a strategy will come at the expense of communicating clearly to everyone else in the room”, I don’t completely agree. I think the people in the room that you want feedback from are the specialists and the experts. So it’s important to find a balance between losing the general audience and wasting this opportunity to communicate with your peers.

I might be in the minority here, but I would rather sit through a few methods slides that I can’t follow in detail, than to sit in a talk in which the methods are so cursory as to be uninformative. Similarly, utterances like “…and then there was some math here, but don't worry I won’t talk about it” seems counter-productive. Ignoring the anti-math sentiment (which reinforces the idea that math is hard and so should be avoided), if the math or stats are important enough to mention, they are important enough to talk about properly. With care, it is generally possible to find a balance in which you provide details for the informed listener while explaining the general logic of the mathematical approach for the rest of the audience. This is true for complicated methods of all types – all listeners should emerge feeling as though they understand what you did, even if they don’t understand it at the same level.

For new speakers this may sound overwhelming. A few points help all talks. Most importantly, every good talk has a compelling narrative that takes the listener on a journey. Even when that journey is complex or has a few twists, speakers can help by signposting important points and findings. Have important information on each slide be both written and verbalized. Get feedback from someone who is not you. And recognize – as a presenter and as a listener—that as with all things, it takes time to become an expert. And, practice makes perfect.

Friday, August 21, 2015

#ESA100: The next dimension in functional ecology

The third day of ESA talks saw an interesting session on functional ecology (Functional Traits in Ecological Research: What Have We Learned and Where Are We Going?), organized by Matt Aiello-Lammens and John Silander Jr.

As outlined by McGill and colleagues (2006), a functional trait-based approach can help us move past idiosyncrasies of species to understand more general patterns of species interactions and environmental tolerances. Despite our common conceptual framework that traits influence fitness in a given environment, many functional ecology studies have been challenged to explain much variation in measured functional traits using underlying environmental gradients. We might attribute this to a) measuring the ‘wrong’ traits or gradients, b) several trait values or syndromes being equally advantageous in a given environment, or c) limitations in our statistical approaches. Several talks in this organized session built up a nuanced story of functional trait diversity in the Cape Floristic Region (CFR) of South Africa. Communities are characterized by high species but low functional turnover (Matt Aiello-Lammens; Jasper Slingsby), and only in some genera do we see strong relationships between trait values and environments (Matt Aiello-Lammens; Nora Mitchell). Nora Mitchell presented a novel Bayesian approach combining trait and environmental information that allowed her to detect trait-environment relationships in about half of the lineages she investigated. These types of approaches that allow us to incorporate phylogenetic relationships and uncertainty may be a useful next step in our quest to understand how environmental conditions may drive trait patterns.

Another ongoing challenge in functional ecology is the mapping of function to traits. This is complicated by the fact that a trait may influence fitness in one environment but not others, and by our common use of ‘soft’ traits, which are more easily measurable correlates of the trait we really think is important. Focusing on a single important drought response trait axis in the same CFR system described above, Kerri Mocko demonstrated that clades of Pelargonium exhibited two contrasting stomatal behaviours under dry conditions: the tendency to favor water balance over carbon dioxide intake (isohydry) and the reverse (anisohydry). More to my point, she was able to link a more commonly measured functional trait (stomatal density) to this drought response behavior.

Turning from the macroevolutionary to the community scale, Ben Weinstein evaluated the classic assumption of trait-matching between consumer (hummingbird beak length) and resource (floral corolla length), exploring how resource availability might shape this relationship. Robert Muscarella then took a community approach to understanding species distributions, testing the idea that we are most likely to find species where their traits match the community average (community weighted mean). He used three traits of woody species to do so, and perhaps what I found most interesting about this approach was his comparison of these traits – if a species is unlike the community average along one trait dimension, are they also dissimilar along the other trait dimensions?


Thinking of trait dimensions, it was fascinating to see several researchers independently touch on this topic. For my talk, I subsampled different numbers and types of traits from a monkeyflower trait dataset to suggest that considering more traits may be our best sampling approach, if we want to understand community processes in complex, multi-faceted environments. Taking trait dimensionality to the extreme, perhaps gene expression patterns can be used to shed light on several important pathways, potentially helping us understand how plants interact with their environments across space and time (Andrew Latimer).

To me, this session highlighted several interesting advances in functional ecology research, and ended with an important ‘big picture’. In the face of another mass extinction, how is biodiversity loss impacting functional diversity (Matthew Davis)?



McGill, B. J., Enquist, B. J., Weiher, E., & Westoby, M. (2006). Rebuilding community ecology from functional traits. Trends in ecology & evolution, 21(4), 178-185.

Thursday, August 13, 2015

#ESA100 The big-data era: ecological advances through data availability

Ecology is in a time of transition –from small-scale studies being the norm to large, global datasets employed to test broad generalities. Along with this ‘big data’ trend is the change in the ethical responsibility of scientists who receive public funds to share their data and ensure public access. As a result big online data repositories have been popping up everywhere.

One thing that I have been doing while listening to talks, or talking with people, is to make note of the use of large online databases. It is clear that the use of these types of data has become commonplace. So much so, that in a number of talks, the speakers simply referred to them by acronyms and we all understood what it was that they used. Here are examples of online data sources I heard referenced (and there are certainly many more):



 It seems difficult to keep track of all the different sources of available data, and these repositories differ in their openness to public access, with some requiring registration, permission requests, and the requirement to include data submitters as authors on publications. With Genbank as the gold standard for a data repository, it is inevitable that other types of ecological data will soon be required to be freely available. I've never figured out why genetic data has different accessibility expectations than, say, leaf trait data.

Despite the attractiveness of huge amounts of data available online, such data can only paint broad pictures of patterns in nature and cannot capture small scale variability very well (Simberloff 2006). We still require detailed experiments and trait measurements at small scales for things like within-species trait variability.

Ecology has grown, and will continue to do so as data is made available. Yet, the classic ecological field experiment will continue to be the mainstay for ecological advancement into the future.



Simberloff, D. (2006) Rejoinder to Simberloff (2006): don't calculate effect sizes; study ecological effects. Ecology Letters, 9, 921-922.

Wednesday, August 12, 2015

#ESA100 Have system -need science! The opportunities for green roof ecology

 Green roofs are now a mainstay of urban green infrastructure and a tool to promote sustainable urban development. A number of municipalities, including Toronto-where I live, now have bylaws or policies requiring green roofs on certain types of infrastructure. The rationale for these requirements is that green roofs provide direct energy savings, reduce albedo, reduce storm water runoff, and support other ecosystem functions and provide wildlife habitat. But it is these last two –the ecological benefits, though often touted, lack clear evidence. I attended an organized oral session on green roof biodiversity organized by Whittinghill, Starry and MacIvor, and it was clear from the presentations that people were excited by the opportunities for ecological research. More importantly, they made the case that we know so little about these systems, and research is desperately needed to guide policy –we simply need more ecologists working on this problem.

Chicago City Hall green roof, adapted from Wikipedia (CC-BY-SA 3.0)
I would argue strongly that urban systems, like green roofs, are understudied and that these systems are the very places that ecological concepts and theories can have relevance. My medical colleagues study human physiology or microbiology in order to cure sick people –their science has direct application to improving the world and human well being, and ecologists have the same opportunity. Like a sick patient, urban systems are where our science can have the greatest impact and can provide the most benefit. Urban systems are under direct management and provide ample opportunity to manipulate ecological patterns and processes in order to test theory and manage societal benefits.


Time to study cities!

Tuesday, August 11, 2015

#ESA100 Declining mysticism: predicting restoration outcomes.

Habitat restoration literature is full of cases where the outcomes of restoration activities are unpredictable, or where multiple sites diverge from one another despite identical initial restoration activities. This apparent unpredictability in restoration outcomes is often attributed to undetected variation in site conditions or history, and thus have a mystical quality where the true factors affecting restoration are just beyond our intellect. These types of idiosyncrasies have led some to question whether restoration ecology can be a predictable science.

Photo credit: S. Yasui


The oral session “Toward prediction in the restoration of biodiversity”, organized by Lars Brudvig, showed how restoration ecologists are changing our understanding of restoration, and shedding light on the mystical qualities of success. What is clear from the assembly of great researchers and fascinating talks in this session is that recent ecological theories and conceptual developments are making their way into restoration. Each of the 8 of 10 talks I saw (I had to miss the last two) added a novel take on how we predict and measure success, and the factors that influence it. From the incorporation of phylogenetic diversity to assess success (Becky Barak) to measuring dispersal and establishment limitation (Nash Turley), and from priority effects (Katie Stuble) to plant-soil feedbacks (Jonathan Bauer), it is clear that predicting success is a multifaceted problem. Further, from Jeffry Matthews talk on trajectories, even idiosyncratic restoration trajectories can be grouped into types of trajectories (e.g., increasing diversity vs plateauing) and then relevant factors can be determined.


What was most impressive about this session was the inclusion of coexistence theory and basic demography into understanding how species perform in restoration. Two talks in particular, one from Loralee Larios on coexistence theory and the other from Dan Laughlin on predicting fitness from traits by environment interactions, shed new light on predicting restoration. Both of these talks showed how species traits and local environmental conditions influence species’ demographic responses and the outcome of competition. These two talks revealed how basic ecological theory can be applied to restoration, but more importantly, and perhaps under-appreciated, these talks show how our basic assumptions about traits and interactions with other species and the environment require ground-truthing to be applicable to important applied problems.

Monday, August 10, 2015

ESA#100 Day 1: The bar is set high

Day 1! This is as good as you will feel - tomorrow and beyond sleep be in will decline and hangovers will rise. Today there was only a half day of talks, but they were a strong start to the week.


There was a great organized section on "Community and Ecosystem Effects of Rapid Evolution" that made a conclusive case for the frequent and meaningful effects of evolution over short timescales on the community or ecosystem. Examples ranged from Darwin's finches, where Sofia Carvajal Endara made at initial attempts to consider how feedbacks from finch evolution and character displacement affected species and trait diversity in seed plants. Martin Turcotte consider the issue in terms of agricultural domestication and the implications for herbivores. He obtained an impressive 29 species' pairs, representing a domesticated species and its ancestor and carried out trials, including one in which an aphid species was grown for multiple generations on the ancestral member of each pair, then switched to the domesticated species. There was no directional evolution observed for the aphid species, but their evolution slowed down on crop plants. Aphid abundances tended to be higher on crops, and simulations suggested that selection was higher on the wild plants, and so was genetic drift. As a final example, Erica Holdridge looked at protist (Colpidium) microevolution, and her results reminded us that many of the protist experiments in the past likely included both evolutionary and ecological effects. Hopefully this is a topic that will continue to grow in the future.

Random notes: I always try to see what I like in talks so I can emulate them. Today I noticed a number of speakers for whom confidence and careful, practiced wording went a long way, even on talks where the concepts were very difficult. 

Favourite quotes (unattributed for anonymity):

Use of "2 cents" to title that section where you extrapolate your results to bigger-picture discussion.

"Community ecologists always want more than two species, although, two species is a good starting point." (absolutely!)

"The data isn't very good; it doesn't support the model"