Title: Size Ratios
1(No Transcript)
2Size Ratios
- Much of the size ratio literature is based on
simple univariate measurements of body size or a
single character, and that may be misleading or
simplistic (why?) - For example, tests of morphological patterns
frequently yield different results depending upon
which character was used - Additionally, most morphometrics are highly
correlated
3Size RatiosMultivariate Analyses
- Consequently, it may be more advantageous to use
multivariate analyses of morphological pattern to
gain insight into possible community structure
4Size RatiosMultivariate Analyses
- There are a variety of multivariate methods
- For example, Principal Components reduces the
dimensionality of the dataset and maximizes
amount of variation explained or Discriminant
Analysis (maximize separation between groups)
5Size RatiosMultivariate Analyses
- Unfortunately a common practice is to represent
species as points in multivariate space, drawing
polygons (or amoebas) around groups of species
and offering some post hoc explanation for the
groupings
6Size RatiosMultivariate Analyses
- However, there are still null models that can be
generated to compare patterns of community
structure from random patterns
7Size RatiosMultivariate Analyses
- Two types of community structure have been
inferred from multivariate analyses of morphology - 1) overdispersion of morphology (assumed to
reflect competition), analogous to size ratio
analyses (measured within a community) - 2) convergence of morphology (typically measure
between communities)
8Size Ratiosoverdispersion of morphology
- Gatz (1979) examined 56 morphological characters
measured for co-occurring stream fishes - Null assemblages were constructed by choosing
random points along each factor axis and then
projecting them into the morphological space
(Euclidian distance very similar to RA1, where
resource utilizations are replaced with random
number and always get a relatively high)
9Size Ratiosoverdispersion of morphology
- Of note, he also analyzed Euclidian distances
between sympatrically occurring members of a
single family or genus and obtained comparable
results
10Size Ratiosoverdispersion of morphology
- Ricklefs and Travis (1980) constructed 2 null
models drawing species lists from a larger
source pool and maintaining observed
morphological features or randomly generating
synthetic species by substituting each factor
score with a random, normal deviate. - Species packing was measured by the average
nearest-neighbor distance and evenness as the
standard deviation of this metric
11Size Ratiosoverdispersion of morphology
- Applying this protocol to avian communities, mean
nearest-neighbor distance were generally less
than expected, whereas standard deviations
usually matched the predictions of the null model
(Fig. 6.10)
12Results varied widely with island communities
being overdispersed
13Size RatiosConcordance of Morphology
- These studies involve 2 assemblages of unrelated
species in similar environments - One option would be to test for ecological
equivalent sets of species - Null Model differences in body size of species
matched between two assemblages are no smaller
than would be expected by chance
14Size RatiosConcordance of Morphology
- Size distributions were too close to be
expected by chance - However, concordance may not be best test for
similarity
15Size RatiosMorphology and Abundance
- Previous assumption morphology and resource use
are intimately related and competition is so
strong, cannot coexist - Morphology and abundance of coexisting species
may not result in competitive exclusion - However, numerous studies have not supported this
hypothesis originally
16Size RatiosEvolutionary Extinction Morphology
- One problem with analyzing present-day
assemblages is extinctions or shifts in
morphology are not observed but must be inferred
indirectly
17Size RatiosEvolutionary Extinction Morphology
- Fossil assemblages can give insight into
long-term patterns of extinction and morphology - For example, are extinctions random with respect
to morphology or are species that are too close
to one another more likely to go extinct?
18Size RatiosEcological Extinction Morphology
- In ecological time, can extinctions be predicted
on the basis of morphology or other species
attributes? - Many (e.g. conservationists) would be very
interested in knowing if extinctions are random
with respect to body size, habitat affinity, or
trophic status
19Size RatiosExample of Ecological Extinction
- Moulton and Pimm argued that extinction of
introduced species in the Hawaiian Islands could
be predicted on the basis of body size or
morphology, chiefly resulting from competition
from introduced species
20Size RatiosExample of Ecological Extinction
- For example, introduced pairs of congeneric
species that both survived on at least one island
(n6) differed more in bill length (22) than
congeneric pairs in which one of the pair went
extinct (9 n9) - Introduced species were overdispersed in
morphological space compared to random draws of
species from the set of all introduced forest
passerines
21Size RatiosExample of Ecological Extinction
- Introduced finches of Oahu and introduced
passerines in Tahiti also exhibited morphological
overdispersion - Fig 6.12. Surviving species
- (filled squares) were significantly
- overdispersed in comparison
- to random communities
- However, not so
- clear-cut
22Size RatiosEmpirical Tests
- The size ratio controversies have not only
addressed size overlap and better statistical
tests, but they have begun to account for other
sources of variation known to influence the
mechanisms driving these patterns (e.g.
geographic variation in morphology, patterns of
resource use)
23Size Ratios Empirical Tests
- Ecological Character Displacement in the Red Fox
(Dayan et al. 1989) - Competition and Morphology of Co-occurring
Dytiscid Beetles (Juliano and Lawton 1990) - Bill Sizes of Galapagos Finches (Lack 1947, Grant
1972)
24(No Transcript)