Transcript Slide 1

Vegetation Patterns of the
Tallgrass Prairie: A Proposal
Daniel McGlinn
Map courtesy of
PG Earls
McGlinn 2005
Outline
• Introduction
– The Species pool hypothesis and turnover
• The Tallgrass Prairie Preserve
– Management methods and goals
• Species-area and species-time theory
• Preliminary analyses: diversity through space
and time
• Future Questions
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Species pool hypothesis
Speciation
large-scale migration
small-scale migration
Filtering
dispersal
Abiotic factors and
Biotic interactions
Actual species pool
Local species pool
Regional species pool
Redrawn from Zobel 1997
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Development of Species-pool
hypothesis
• Importance of regional species pool
– Zobel 1997
• Evolutionary or historic soil conditions determine
local species richness (SR)
– Pärtel 2002 and Ewald 2003
• Exotics may provide key insight
– Palmer 2003
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Field of Dreams hypothesis
• Special case of Species-pool hypothesis
– Palmer et al. 1997
• If you build it (disturbance regime), they will
come…
– Evolutionary pattern of burning and grazing
• Predicts an increase in natives and a decrease
in abundance and richness of exotics
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Species pool hypothesis
Speciation
large-scale migration
small-scale migration
Filtering
dispersal
Abiotic factors and
Biotic interactions
Actual species pool
Local species pool
Regional species pool
Redrawn from Zobel 1997
McGlinn 2005
Turnover
• Species level
– Carousel model: van der Maarel & Sykes 1997
– Mobility indices: Palmer and Rusch 2001
• Community level
– Species-area curve: Watson 1859
– Species-time curve: Preston 1960
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Community level turnover
• Species-area and species-time
relationships
– Preston’s (1960) ergodic conjecture –
Rosenzweig 1995,1998
– Tested for time-space interaction – Adler and
Lauenroth (2003)
– Sampling and ecological effects – White (2004)
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The Tallgrass Prairie Preserve
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15,000-hectare natural area
Owned by TNC since 1989
Bison introduced 1993
Randomized burning regime began 1993
• Ecological goal:
– To create a heterogeneous landscape that
contains the full compliment of native species
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Current data
• UTM grid 1997-2000
• 20 quadrats resampled 1998-2004
– Plots chosen randomly with criteria that it not
have any woody cover, standing water, or
>20% rock cover
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10 m
Map courtesy of PG Earls
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Randomized Burning
• Simulate the presettlement fire frequency
and seasonality
• Burn units selected randomly from areas
with a minimum fuel load
• Creates a spatially and temporally
dynamic landscape
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Species-area and Species-time
•
Structure of the equation
– c, z, and w values
•
Empirical results
– linearity and nonlinearity
•
Mechanisms drive patterns
– Statistical, ecological, evolutionary
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Structure of SAR
log S  log c  z log A
• c and z values;
• c is often only interpreted as a mere
intercept
• Non-linear form of SAR shows that c
actually helps to determine the slope
S  cA
z
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Structure of STR
• Same as SAR
log S  log c  w log T
S  cT
w
• Rate of species accumulation is w
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Empirical curves from the TGPP
Fig from Palmer et al. (2003)
Log # Species
z = 0.30
Log Area
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Empirical patterns
Rosenzweig 1995
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TGPP quadrat scale
Preston 1960
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Current findings
• Species richness has significantly increased in
the twenty 10x10 plots from 1998 to 2004
• SAR is slightly convex in log-log space
• STR more linear in log-log space
• The rate of species-accumulation decreases at
the same rate for increasing area and increasing
time
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Mean r2 = 0.9816
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Mean r2 = 0.9982
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Decreasing rate of species
accumulation
Slopes of species-time curves
w
z
Slopes of species-area curves
log T
log A
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Remaining questions
• Continue to resample plots
– When does ecological change begin to take place
– How does fire and grazing effect the shape of this relationship
• At what scale do spatial and temporal accumulation of
species seem equivalent?
– Is this the same as for Konza (47 m2)?
• Is the way that organisms move from one location to
another analogous to their ‘movement’ through time?
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Questions
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Other explanations abound…
• Exotics maintain or increase
– A more heterogeneous landscape structurally
provides more niches
– Exotics are inherently generalists and can
adapt rapidly to new environments – highly
plastic phenotypes