The Statistics and Biology of Species-Area Relationship (Connor and McCoy 1979)



The Statistics and Biology of the Species-Area Relationship (Connor and McCoy 1979) cited 2,376 times

Commentary by Brian A. Maurer (1954-2018)

  • co-founded the discipline of macroecology in the famous 1989 Science article (Macroecology: The Division of Food and Space Among Species on Continents)
  • director for statistical training and consulting at Michigan State University
  • 69 peer-reviewed publications and 2 books (Geographical Population Analysis: Tools for the Analysis of Biodiversity 1994; Untangling Ecological Complexity: The Macroscopic Perspective 1999)
  • professor and mentor of undergraduates, grad students, and postdocs 
  • talented singer, songwriter, guitarist
Education: 
  • BS in Zoology (Brigham Young University,1977)
  • M.S. Wildlife Management (1980, West Virginia UniversityThesis Topic:  Avian foraging and habitat structure.) 
  • M.S. Statistics (1982, University of ArizonaThesis Topic:  Repeated measures in bioassay.) 
  • Ph.D Major Wildlife Ecology, Minor EEB (1984, University of ArizonaDissertation Topic:  Environmental heterogeneity and avian community structure.)


    Career:  1984-1986 postdoc University of Arizona with Jim Brown; 1986-1999 professor in Zoology, Bringham Young University; 1988 Visiting Scientist, Lanzhou University, China;  1994-1995 research associate in community ecology, Museum of Natural History at University of Kansas; 1997 distinguished researcher in residence, Mountain Research Center at Montana State University; 1999-2018 professor department of fisheries and wildlife at Michigan State University; 2012-2018 director for statistical training and consulting at Michigan State University

    Main Authors:


    Edward F Connor (left): plant- insect interactions, population ecology, quantitative ecology, biogeography, macroecology
    Professor in Biology Department at San Francisco State University

    Earl D McCoy (right): biogeography, biostatistics, conservation, restoration 
    Ph.D., Florida State University, 1977
    Professor at University of South Florida


    Paper Notes

    History: Continuation off of work from Frank Preston (1948) who first described number of species in a community to be a log-normal distribution which later arrived at relation of power relation between species number and area.
           ---> Then was used for MacArthur and Wilson's "equilibrium theory of island biogeography" (species number is a dynamic result fo immigration or extinction or a combination of both)
    Conceptual figure of equilibrium theory of equilibrium theory of
     island biogeography

           ---> Also was accepted at the time that number of species increased with area  and that number of species in a taxa increase with decreasing latitude. 


    Theory Implications: conservations Single Large Many Small

    Novelty: This paper is novel because Connor and McCoy sought out to quantitatively test these theories through a combination of 100 data sets

    Summary
    • No unifying theory to explain SAR. All depends.
    • Studies vary on which model fits the data best though power function suggested. 
    • Slopes and intercepts vary between datasets- skeptical of biological interpretation.
    • Equilibrium theory should be used as a testable hypothesis. It doesn't fully explain causality and shouldn't be accepted as fact.
    • Latitudinal-diversity relationship can be seen in correlation coefficients and not explained by intercept (alpha diversity) or slope (beta diversity).
    • Interpretations of SAR should be based on 1) best model fit for the dataset, 2) correlation between number of species and area, 3) how parameter values compare to those published in the literature.

    Is there a unique theory to explain Species Area Relationship (SAR) Theory?
    3 Main Hypothesis of SAR:
    1. Habitat- diversity (Williams 1964): as area sampled increases so does chance of getting more habitat thus species ++. With area+
    2. Area-per se (Preston 1960, 1962; MacArthrur &Wilson 1963,1967): species# is from immigration and extinction rates not habitat. Immigration is independent of island size but more dependent on proximity to source population, and Extinction is inversely proportional to population size which is also related to area.
    3. Sampling: null hypothesis...sampling phenomenon not biological- tend to sample large areas more.
           -----------> All have been supported in the literature around this time.  All must be taken into consideration, thus mechanism not exactly resolved.


    Is there a best fit model?
    Conventional SAR models tested with datasets
    • species/area (S/A)... aka untransformed
      • S= k +zA
    • species/log_area (S/LA)... aka exponential
      • S = log k + z log A
    • log_species/area (LS/A)... aka untransformed
      • log S = k + zA
    • log_species/log_area (LS/LA)...aka power function**
      • S = kA^z
     --> Not exactly.. Power is better than exponential but the same as untransformed. However, there doesn't seem to be a pattern that discerns what model is best. Power model is suggested to continue to be used.

    Can parameters of  power function  be interpreted-biologically and statistically?
    Other studies have argued for biological significance for intercept and slope of the power function
    • Preston's power function  implies significance with the "caonical" slope of 0.262
      •  Evaluation of 100 studies show this range of slope should ultimately be 0.20-0.40 which may be coincidence, but also is a trend seen regularly in biology. Should be used as a “criterion of subtraction” aka null slope values, where deviation from this range might mean something biologically.
    • Slope and intercepts in a power function are interdependent so only intercepts can be compared.
    • Slope 1= isometric relationship, <1= diminishing return or area for species , >1 = greater # species in larger areas
    • Slope and intercepts of previous power functions not always true so not generalizable- view as fitted constants with no biological relevance

    Interpretation of SAR (methods)?
    • Correlation should be used if interested in degree of relatedness between species and area but regression should be used if comparing 2 or more bivariate distributions
    • Parameter estimation: least-squares regression and reduced-major-axis method (geometric mean) 
      • least squares regression chosen because yield similar slopes and intercepts
        • Model I regression- only dependent variable assumed to have error but there’s often error in area which then underestimates slope
        • "Berksen case" (error permitted but controlled by experimenter via chosen sizes) 
        • **Model II: error  uncontrolled which is preferred for SAR
          • Model II  should be used when trying to get parameter estimates, while Model I or II can be used for comparing parameter values


    Islands vs continents/ isolated vs non isolated: 
    Figure 3 in paper A on left and B on right
    Figure 4 in paper: Slopes can be same even if intercept
    starts off smaller for far isolates as opposed to near

    Fig 3A: transient hypothesis (MacArthur and Wilson's view)- slopes will be smaller in non-isolated areas (within continental area or within an islands) due to many transients that will be encountered which decreases likelihood or achieving more species when expanding area.

    Fig 3B: Schoener's view- slope is dependent on source pool of species - "distant archipelagoes have depauperate biotas"

    However, slopes can still be the same if y intercepts are different for isolates (fig4)


    -----> Both views are supported in the literature.








    Alpha and Beta Diversity into slope and intercept parameters
    Intro to Alpha/Beta/Gamma diversity: conceptual figure describing Whittaker's 1960 ideas on diversity found from: https://www.webpages.uidaho.edu/veg_measure/Modules/Lessons/Module%209(Composition&Diversity)/9_2_Biodiversity.htm
    MacArthur and Wilson attempted to intertwine Whittaker's theory for interpretation in analysis by suggestion that alpha could be intercept (within island/habitat diversity) and beta could be slope (between islands/habitat diversity) .
    ----> But importance of alpha vs beta diversity in SAR trend is impossible to pull apart bc slope and intercept of the power function are interdependent… 

    Latitude
    MacArthur tries to use this theory to explain the inverse relationship between latitude and species number (but the same issues of slope and intercept interdependency exists)
    • if intercept is related: pattern is driven mostly by increase within-habitat diversity
    • if slope is related: increased between-habitat diversity
    • if both intercept and slope: latitudinal-diversity gradients are driven by both within and between habitat diversity
    ---> Slope and intercept were tested but few to no datasets showed particular pattern in datasets.
    However, correlation coefficients are negatively correlated with latitude (r=-0.3183, P<0.001; see figure 5 below); meaning log area explains more variation in log species at low latitude than at high latitudes. 


    Figure 5- correlation decreases with latitude

    Discussion Points:


    1. Can you think of any confounding factors that could change this general pattern of species increasing with area?
    2. Considering what has been stated by theory on continuous vs separate habitats, do you agree with the general transient hypothesis? Could you think of ways that having many transients might not lead to an overinflated species numbers in small areas?
    3.  Do you think you might find the same patterns on smaller scales and global scales?





    Comments

    Kevin Willson said…
    1. As was mentioned earlier in the post, the sampling patterns that are available between small and large areas may affect the trend. The number of unique ecosystem patches that are encountered may change, which will strongly impact the number of species found. The type of plant/animal that you are trying to describe will also influence species richness over area, as birds will have different patterns relative to mammals relative to insects relative to woody plants.
    2. I think that the general transient hypothesis might be applicable across some areas under the right condition, but as this paper broadly pointed out, there are too many examples of trends not following the transient hypothesis to make it applicable as a macroecological idea. One reason we might not see an overinflated species count in a specific area is because there are not enough resources that are found in other nearby areas to support the transient species (like a desert or large rocky outcrop). Another reason for a difference is a drastic shift in the ecosystem (like change from forest to ocean or grassland to a large lake) that does not allow for as many species to overlap as would be expected otherwise.
    3. I think what this paper really pointed out well is that there may be some patterns that will never actually exist across any scale, no matter how hard we look or how badly we want to see one. I was not sure what pattern was being asked for, but in the context of this paper, I would assume not given their argument.

    Overall, I appreciated that thorough job of the authors quantitatively explaining that there was no evidence that there was a macroecological pattern between area and species richness. They took on theory presented by very important people in the field and showed that the theories did not hold water when tested against large datasets.
    Keara Bixby said…
    Like Kevin said with ecosystem patches, the available niche space could change the overall pattern of species increasing within an area. Area may increase but the amount of actual suitable habitat may change depending on the organism you are sampling for. In the conclusion of the paper they state there may not ever be a single best-fit model but that it allows for some comparisons across different geographic areas on a general basis. I feel that this is the theme in ecological problems “it just depends”. I would imagine that you could find some sort of trend that could be statistically manipulated to parallel the findings in this paper.
    liz said…
    1: The species-area relationship makes sense but could definitely have some confounding factors because each species is unique. For example, migratory species could affect species richness depending on the sampling methods used. Additionally, ecosystem patches or microhabitats can change as area increases, meaning the areas of suitable habitats for certain species can actually decrease.
    2: I don't think I really agree with the transient hypothesis, especially at a large scale. Species that are transient at one location may be core species in another location, so it doesn't seem like the transient hypothesis could work from a macroecological perspective. I haven't often heard of transient species causing an inflation in species richness, though they are known to alter the slope of species-area relationships. I think some ways that having transients could not lead to inflated species richness could be when there is more heterogenous habitat present, or when organisms can't keep up a positive population growth rate in small scales or in areas with limited resources.
    3: I think the species-area relationship generally holds true at many different scales, but I'm sure the patterns mentioned in this paper will vary because every species and habitat found on earth is unique.

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