- Kraft N.J.B. et al. 2011. “Disentangling the Drivers of β-Diversity Along Latitudinal and Elevational Gradients” Science. Vol. 333:6050 pp.1755-1758
- Qian. H. et al. 2012. Comment on “Disentangling the Drivers of β Diversity Along Latitudinal and Elevational Gradients”. Science 30:1573.
- Tuomisto, H. and Ruokolainen, K. 2012. Comment on“Disentangling the Drivers of β Diversity Along Latitudinal and Elevational Gradients”. Science 30:1573.
- Kraft N.J.B. et al. 2012. Response to Comments on“Disentangling the Drivers of β Diversity Along Latitudinal and Elevational Gradients”. Science 30: 1573.
A good scientific debate makes for excellent spectator sport
(although it’s probably less fun for the participants). Many of the best
ecological debates are now classics of the literature—Diamond vs. Simerberloff,
Lawton vs. Simberloff, Hubbell vs. many—and these historical debates influence present day ecology. Interestingly, debates in ecology seem to revolve
around two particular issues: whether the data is appropriate and whether the
methods are adequate to draw conclusions about a particular process.
As an example, there’s a typical ecological debate occurring
in Science over Kraft et al.’s “Disentangling the drivers of β-diversity
along latitudinal and elevational gradients”. In this paper, the authors
reevaluate the mechanisms that drive changes in species identity along
latitudinal and elevation gradients using a null model. Although β-diversity
may vary along biogeographical gradients as a result of processes such as
dispersal limitation, range size, and habitat filtering, total (γ) diversity
also varies along these gradients (we know that richness is generally higher in
the tropics and the lowlands). Since this suggests that γ- and β-diversity
aren’t independent, it may be that changes in γ-diversity need to be accounted
for as an explanation for changes in β-diversity (Chase 2011). When Kraft
et al. controlled for γ-diversity using a null model, they found that the
magnitude of β-diversity did
not vary along latitudinal or elevational gradients. They stated that this
means: “there may be no need to invoke differences in the mechanisms of community
assembly in temperate versus tropical systems to explain these global-scale
patterns of β-diversity.”
This conclusion is in contrast to multiple papers that have
suggested that tropical communities are somehow structured differently from
temperate communities. Such work has been far from conclusive, however, finding
evidence for everything from stochastic assembly to microhabitat-driven
assembly in tropical regions. However, given the strong conclusion from the Kraft
et al. paper, it’s not surprising that there were several responses from other
researchers of β-diversity (Tuomisto and Ruokolainen and Qian et al.). It’s
also not surprising that the points raised in these responses are fairly
typical for debates in community ecology, calling into question the suitability
of the data, the appropriateness of the spatial scale for capturing the
processes of interest, and the question of whether the methods are correct. The
debate is as much about the fundamental questions of how we define and measure β-diversity
as it is about the particulars of the Kraft et al. article.
For example, both Tuomisto and Ruokolainen and Qian et al.
questioned the sampling design of the data, as to whether there was too much
within-plot variation (Tuomisto and Ruokolainen) or, alternately, too little
between-plot variation (Qian et al.) to correctly capture the amount of β-diversity.
Tuomisto and Ruokolainen further suggested that the plots used in the original
study undersample local (α) diversity and therefore overestimate the
differences between plots. Both sets of authors suggest that inappropriate
sampling would make it difficult to generalize Kraft et al.’s results to other
studies of β-diversity. Kraft et al.’s response was that although plots are
placed to minimize among-plot environmental variation, this does not make them
inappropriate to test for finer scale evidence of environmental processes, and
that β-diversity still varies markedly between plots. However, given that this
debate - about whether there is a “best” spatial scale at which to examine the
ecological causes of β-diversity and a “best” way to sample to capture
variation among communities – is occurring among experienced β-diversity
researchers suggests that these are still fuzzy areas.
Another aspect of this debate relates to the ongoing
discussion about the appropriate definition and calculation of β-diversity
(Tuomisto 2010). The most traditional methods define β-diversity as a
multiplicative or additive function of α- and γ-diversity, and Kraft et al.
argue that as a result β-diversity is not independent of those variables. To
account for this fact, Kraft et al. use a null model that incorporates γ-diversity, to predict β-diversity under random or stochastic assembly. However,
Tuomisto and Ruokolainen argue that the measure of β-diversity used (βP =
1 – α/γ) is such that γ-diversity can vary without affecting β-diversity,
provided alpha-diversity is also free to vary. However, Kraft et al. dispute
this, suggesting that perfectly scaled changes in both γ- and α-diversity, such
that β-diversity remains unchanged, represent a special case that does not
appear in their data set.
Of course, other points were discussed among the authors.
Qian et al. disagreed with the use of latitudinal gradients, noting that the
ecological “meaning” of a given latitude is rather vague. However, given that
the authors admit their site data is likely to capture small-scale variation in
β-diversity, it seems that trying to relate their results to large-scale
latitudinal or elevational gradients is a greater issue.
Kraft et al. suggested in their response that many of the
criticisms were misunderstandings of the methods and findings of the original
paper. You might more correctly say that disagreements like this capture
important weaknesses or ambiguities in current understanding and theory. It’s
true that at their worst, debates create conflict and that since responses are
rarely peer-reviewed to the same extent the original publication is, too much
weight may be given to meritless counter-arguments. However, good debate should
drive progress, force researchers to reevaluate their assumptions, and
ultimately hold science accountable. And for that reason it should be
encouraged.
**I should note that this post is specifically meant in
relation to debate among researchers, not to situations where scientists are in
agreement and the debate is occurring in the public sphere.
6 comments:
Not to crush your youthful idealism ;-), but a reasonably large fraction of debate in ecology and evolution is anything but open, honest, and productive:
http://oikosjournal.wordpress.com/2012/03/22/trying-to-save-a-zombie-idea/
http://sociobiology.wordpress.com/2012/04/06/agreement-and-disagreement-in-social-evolution-insight-from-david-queller/
But my youthful idealism is the only thing preventing me from becoming jaded and cynical ;-)
So obviously yes, there are lots of unfruitful debates in ecology (and for the life of me, I can't figure out why people are so invested in the curved productivity richness relationship, when no good mechanism has been suggested for such a thing). But the reverse of that, that there is never debate, seems a lot worse to me. And the PRR example you link could just as easily be seen an example of how debate does work - if debate hadn't existed about PRR (particularly from papers like Abrams 1995) it would be probably be going strong today. I guess I'm not convinced that debate is necessarily harmful, but I'm convinced that the absence of debate is.
There actually are good mechanisms for a humped diversity-productivity relationship. Standard keystone predation models predict this; see, e.g., Leibold 1996 Am Nat. So does the Levene (1953) model in evolution; see the work of Rees Kassen and colleagues. If you wave your arms you can get a Tilman-type resource ratio model to spit out a humped diversity-productivity curve. But there are of course lots of other models that make other predictions.
Re: unproductive debate vs. no debate, yes, I suppose an unquestioned and universal consensus in favor of an incorrect idea would be even worse than unproductive debate. That this possibility occurred to you, and not to me, may indicate that your youthful idealism is dead and mine is not. Because if that's what you consider "looking on the bright side", your "bright side" is awfully dark... ;-)
Fair enough. I'm sure the reality is that the effects of debate are somewhere between extremely negative and extremely positive.
A small but important correction to the original commentary: Rather than stating “there is no need to invoke differences in the mechanisms of community assembly in temperate versus tropical systems to explain these global-scale patterns of β-diversity.”, the authors' actual statement was a bit less emphatic: “there *may be* no need to invoke differences in the mechanisms of community assembly in temperate versus tropical systems to explain these global-scale patterns of β-diversity.”
Thanks anonymous, although, I should note that in the abstract, the authors stated "there *is* no need...". However, given the abstract of Science papers tend to state things strongly, I've changed the text above to reflect the more moderate statement from the text.
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