Brown, J.H. 1984 - On the Relationship between Abundance and Distribution of Species


Author: James H. Brown

Author of Macroecology
Member of the National Academy of Sciences
Professor Emeritus, University of New México
Professor, University of Arizona - 1975-87
Associate Professor, University of Utah - 1971-75
Assistant Professor, UCLA - 1968-1971
Postdoc at UCLA, 1967-68
Ph.D. at University of Michigan, 1967 - Emmet T. Hooper (Student of J. Grinnell)


Research interests: Scaling biology and macroecology, experimental desert ecology 


Blurb author: Christy M. McCain (Same blurb author from S. Anderson 1977)


Definitions:
Abundance: Local population density. Terms for extremes of abundance: rare and common.
Distribution/range:  spatial distribution. Terms: restricted (local) and widespread


Brown proposes a theoretical model to make predictions about the ecological and
evolutionary consequences of niche dimensionality that can be tested by evaluating
further the three assumptions:  relationships among environmental limiting factors,
patterns of abundance and distribution, and degree of evolutionary differentiation in taxa
for which adequate data are available.


The Theory: Brown addresses two main topics or patterns in this paper:
  • Spatial Variation in Abundance Within Species 
  • Correlation Between Abundance and Distribution Among Species 
- Based on 3 assumptions (the first two relating principally to the first pattern and all three
addressing the second pattern):
1)  “Variations in population density of a species over space is assumed to reflect
the probability density distribution of the required combinations of environmental
variables” → Changes in population density are tied to the likelihood that their
biotic and abiotic niche requirements are available in a certain area. (Hutchinson's
(1957) multidimensional niche for each species)
2)  “ Environmental variation also is autocorrelated” → Tobler's first law of
geography: everything is related to everything else, but near things are more
related than distant things. If this is true, Brown argued, the center of the species
distribution will offer the most optimum environmental conditions, explaining why
the highest abundance of that species is there.
3)  “... closely related, ecologically similar species differ substantially in only one or
a very small number of niche dimensions. This limited differentiation reflects
evolutionary constraints on morphology, physiology, and behavior as a result of
relatively recent descent from a common ancestor.”


Spatial Variation in Abundance Within Species:
Using previous work and data sets of songbirds and plants, Brown shows how population
density across species ranges is going to have its highest frequency in the center of its
range and that frequency is going to decrease towards the edges or boundaries of the
range (Fig 2).


From figure 2. The bottom graph shows mean population density along 4 transects from the center to
the edge of the geographic range (the black cross in the top map).

This form of abundance peaks near the geographic center of their distribution and
declines toward the edges, forming a normal curve (Fig 3).



Environmental independent variables added together create different niche dimensions
and will determine different population densities according to their requirements,
generating normal distributions of density. “As a consequence of their multiple niche
requirements, almost all species have restricted distributions; Often this is a response to
a single variable, which may be abiotic or biotic (predator/prey/competitor density).
This explains why some species distributions change abruptly or are patchy, which are
exceptions to the unimodal distribution of population density (fig. 8).


Is the pattern in figure 7 an artifact of sampling (are abundant species just more likely to
be
found throughout their range)? Brown takes subsamples of datasets and finds that the answer
is no - increased sample size does not affect predicted range size significantly.




Correlation Between Abundance and Distribution Among Species 
    • For closely related and ecologically similar species, the area of the geographic
range is positively correlated with maximum density, average density over the area
where the species occurs, the number of sites inhabited within a local region. 
      • This is explained by the multidimensionality of niches. If a species is able to
survive and reach high densities in a place, then the species will be able to
occur on many different sites, but if a species has narrow requirements and
cannot attain high abundances, the species will be restricted to the few sites
(niches) that are able to satisfy its needs. 
    • As with Hanski (1982), this model can only compare closely related species
(with assumed-to-be similar niches)
    • Mosaic nature of the environment: larger organisms tend to have less dense, more
widely distributed populations, whereas smaller ones attain higher densities and
exhibit more local and patchy distributions
Why he does not agree with Hanski:
Hanski assumes that all sites are equally suitable for all species and that species distributions
among those sites vary randomly over time.
  1. it is highly unlikely that all sites are equally favorable for all species (species different
requirements and tolerances = difference in distributions.
2. Hanski assumes that rare species rely on colonization in order for populations to persist.
Brown argues that this is unrealistic. Not all rare species have the capability for the
dispersal that would be needed to maintain small, isolated populations, and the more
distant populations are the less likely they are to have suitable habitat between them.
3. “... bimodal distribution of frequency of occurrence is almost certainly an artifact of
sampling a small number of sites with a local region.” The bimodal distribution of species
abundance becomes unimodal if the scale is expanded beyond a small subset of the
species’ total range.
General Discussion
Brown viewed this as a qualitative theory that would serve as the framework for future
statistical analyses of organismal diversity. He recognizes that a criticism of this model
may be that it does not incorporate any environmental mechanisms that may limit range
or abundance, but points out that a strength of the model is that there are simply too
many species and too many relationships to adequately consider all of them (enter
macroecology!). 
Brown saw implications for community ecology in this range-wide pattern. It implies that
widespread species are found in communities of varying composition across their range,
and that niches do not evolve in a tight-knit community but rather in many different
settings across a species range. 
Based on his findings, Brown rejects the idea that there is a trade-off between a
generalist or specialist lifestyle. Although this idea predicts that specialists should be
more common within their limited ranges, Brown finds that they are both rarer and less
widely distributed than closely related generalists. He extends this idea to evolution and
speciation, adding that it implies that there is a broad spectrum of evolutionary success
across organisms. 
So, in accordance with biogeographic theory, rarer species are more likely to go extinct.
This begs the question, “...whence come the species that replace them?” Brown uses
some of his own thoughts on diversity in his answer, including centrifugal speciation,
stating that central (large and widespread) populations are resistant to directional
selection, peripheral (small and isolated) populations are more likely to undergo
speciation. These new species have two paths to increasing their distribution: a) the
environment changes or b) they expand their niche by evolving to compete more
effectively with closely related species. 
Brown concludes by exploring how this model of speciation fits four macroevolutionary
trends: stasis in the fossil record, morphological differentiation in the speciation process,
differences in extinction and speciation rates between taxonomic groups, and the
tendency of evolutionary innovations to occur in marginal habitats. 
Questions
1. What environmental variables and population attributes determine the abundance and
limit the distribution of particular local populations? Could we define general determinants for
the distribution of species?
2.  Brown says that “the general relationships between abundance and distribution developed
here eventually should contribute to our understanding of the biogeography, population genetics,
and evolution of species as well as the ecological attributes of populations and communities.”
What does the model that Brown presents here tell you about your own research? Did this paper
help you think about your own research? New questions or possible explanations to findings you
have had
3. What are your thoughts on Brown’s treatment of Hanski’s model? Brown dismisses its conclusions about bimodal distribution as unrealistic for larger scales. If this is the case, does Hanski’s model make any other useful predictions?

Comments

Kevin Willson said…
1. Environmental variables would likely include resource availability, climate, and the type of surrounding environments (if it dramatically changes from one ecosystem to another, that will affect distribution). Population attributes would include the necessity of the population for any specific parts of their niche (if they are very dependent on one specific aspect or need a lot of specific aspects to come together at the same time to survive) then they will be bound to smaller areas that meet their requirements (ie, specialists) than other species that can exist across a broader range of environment types. The specialist might outcompete other species to have higher abundance locally, but lower distribution because of specific needs to succeed.
2. The model that Brown presents correctly predicted what has ended up happening with ponderosa pine distributions over the past 20-30 years, which is a general contraction in its outer geographic range in southern areas. This is widely explained because these southern ranges are not as productive and ideal for ponderosa pine compared to the tree in other parts of its range. These areas were already edge ecosystems for ponderosa because of precipitation totals, but with the further aridity in the areas, they generally have not returned after recent high severity fires.
3. I think Brown made some valid comments about Hanski’s model not being the dominant model over entire geographic ranges, but I don’t think that was the goal of Hanski’s model. This was specifically for local to regional ranges (at most) from what I was gathering from the paper. I think Hanski’s model has persisted well in finer scale ecological theory because it made use insights and informs distributions at local scales.
Carson said…
While reading this paper, I thought of Rabinowitz's 7 forms of rarity in relation to the model Brown was developing. In her model, it holds that species are either abundant or rare throughout their range and habitats, however broad or narrow they may be. In Brown's model, he asserts that all species are relatively abundant and rare in within their ranges depending on how close they are to the core of their range. Perhaps then it is useful to think of species occupying more than one box depending on where they are?

The second tenant of Brown's theory, that abundant species tend to be more widespread overall and rare species tend to be more restricted in range, matches up well with the upper left and lower right boxes of Rabinowitz' forms of rarity. I am having a hard time explaining some of the other's in the context of Brown's model, namely the lower left (large range, wide niche, sparse pop), though I do believe species that fit that description exist. Anyone else have thoughts on this?

Also, I am curious on what others thought about his treatment of generalist vs. specialist species. If his argument is true that there is actually no trade-off that confers an advantage to being a specialist, then why do so many exist? I don't think I buy that specialist species are often the product of geographically isolated populations of generalist species, although its an interesting thought.

Apologies for this being off the rails of the proposed discussion questions....more things to discuss and think about!
Oona said…
1. This is an interesting question, and I think it's difficult to determine all the possible variables that may affect species distributions. Even if we determine all the variables, it's difficult to generalize across species, since in different species, situations, or locations one or some of these variables may be more strongly affecting the species range limits. An example that comes to mind is when considering the species distributions on mountains. There's been some debate about what controls elevational limits, but one hypothesis is that lower elevational limits are more strongly controlled by competition and upper limits by abiotic factors and physiological constraints.

3. During our class discussion I was thinking about Hanski's model fitting within Brown's scheme, particularly when considering regional populations as subpopulations under ecologically different conditions throughout the species geographic range.

Carson, you bring up an interesting question. I agree with you-- I don't really see why specialists would necessarily always come from populations budding off from the edge of the geographic range. Another way to frame this might be to think about specialists as being "left behind" in an isolated population as climatic conditions changed, and the rest of the species range became uninhabitable, but not necessarily from the edge.
Keara Bixby said…
It would be difficult, and amazing if there was one magical answer to that question. It seems as though environmental tolerance through sunlight could be a good place to start. This way you could think about the primary producers and their needs and work your way up trophic levels. Oona talking about elevational gradients probably gets pretty close to a “one size fits all” variable that could determine limits and abundances. I think in looking at those environmental variables it’s important to keep in mind something that Dr. Smith brought up in the zoom call when thinking of ecology as a static field and paleontology as a dynamic. Dynamic because species have a lifespan that is considered overall in their abundance, where in ecology you don’t necessarily consider those lifespans. That’s something I hadn’t really thought of in thinking about how species become rare over time and using these models. (I hope I didn't butcher that comment, as I did find it really interesting)
Brian said…
This made me think about my own research because my model organism is a widespread and prolific specialist on one tree host so determining the environmental variables to capture the range of the species includes the host variabe. This along with far spore dispersal makes determining where to put sample sites to capture individual populations is hard. I also found it interesting his notes on energetics as my study organism is a mutualist and it contributes to the energetics as food for small mammals but how do you characterize its mutualistic nature in a food or trophic web?

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