Interactions between Avian and Insect Herbivore Communities within MOFEP

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Interactions between Avian and Insect Herbivore Communities within MOFEP

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Interactions between Avian and Insect Herbivore Communities within MOFEP –

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Title: Interactions between Avian and Insect Herbivore Communities within MOFEP


1
Interactions between Avian and Insect Herbivore
Communities within MOFEP
  • John Landosky, Robert J. Marquis, Rick Clawson,
    Wendy Gram, Paul Porneluzi, John Faaborg, Julie
    Ryan, Florence DiTirro, Rebecca Forkner, John
    Lill, and Josiane Le Corff
  • University of Missouri St. Louis
  • November 8, 2007

2
Outline
  • What is MOFEP?
  • Insect and avian communities interactions?
  • Preliminary analysis Something there?
  • Refining the analysis

3
What is MOFEP?
4
MOFEP
Whats the best way to harvest timber while
conserving healthy ecosystems?
5
Design
6
Timeline
1996 Treatment applied
1991-1995
1991
2007

Proposed 2011 treatment
1997-2000 Post-treatment data gathered
(full-scale) Post-treatment
1993-1995 Baseline data gathered (full-scale)
Pre-treatment
1991-1992 Baseline data gathered (preliminary)
7
Timeline
1996 Treatment applied
1997-present
1991
2007

Proposed 2011 treatment
1997-2000 Post-treatment data gathered
(full-scale) Post-treatment
1993-1995 Baseline data gathered (full-scale)
Pre-treatment
1991-1992 Baseline data gathered (preliminary)
8
Isa textula (Limacodidae)
Ecosystem health?
9
Avian/Insect Interactions
10
Top-Down/Bottom-Up Interactions
  • Do trophic levels interact?
  • Top-down?
  • Bottom-up?
  • How can we test for interactions with our data?

11
Bird Project
Hypothetical WOTH Observations
  • Crew members cover entire forest using
    birdlines
  • Identify singing males and spot-map
  • Each line walked 10 times during the month of
    June
  • Three independent observations define a bird
    territory

12
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13
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14
Bird Census
15
Common MOFEP Species
16
Insect Project
  • Leaf chewing herbivores on
  • White oak Quercus alba
  • Black oak Quercus velutina
  • Four times per year
  • Early May, and late June, July, and August
  • Over 250 species identified

17
Free Feeders vs. Shelter Builders
Free Feeders
Shelter Builders
18
Bird Census
19
Preliminary Analysis
  • Is there something there?

20
Preliminary Analysis Model
Bird Census
21
Preliminary Analysis Model
  • Bird territory size
  • 200m from center

Bird Census
22
Preliminary Analysis Model
  • Bird territory size
  • 200m from center
  • Bird Effect
  • Sum each species
  • of territories
  • Mating pair weight

Bird Census
23
Preliminary Analysis Model
  • Bird territory size
  • 200m from center
  • Bird Effect
  • Sum each species
  • of territories
  • Mating pair weight
  • Insect stands
  • point in space

Bird Census
24
Preliminary Analysis Model
  • Bird territory size
  • 200m from center
  • Bird Effect
  • Sum each species
  • of territories
  • Mating pair weight
  • Insect stands
  • point in space
  • If gt50 coverage
  • corrected
  • If lt50 coverage
  • excluded

Bird Census
25
Hypothetical Data Slide
rmANCOVA Unstructured Log-transformed Year p lt
0.0001 Ecotype p0.34 Treatment p0.23 Bird
Density (cov) p0.01
Pre-treatment (1993-1995)
Post-treatment (1997-2000)
rmANCOVA Compound Symmetry Log-transformed Year
p lt 0.0001 Ecotype p0.10 Bird Density (cov)
p0.02
y -0.021x 0.342 r2 0.0312
y -0.012x 0.11 r2 0.0127
0.8
0.8
Herbivore Abundance (residuals)
Herbivore Abundance (residuals)
0
0
-0.8
-0.8
30
0
30
0
15
15
Birds w/in 200m
Birds w/in 200m
26
Hypothetical Data Slide
Pre-treatment (1993-1995)
Post-treatment (1997-2000)
rmANCOVA Unstructured Log-transformed Year p lt
0.0001 Ecotype p0.34 Treatment p0.23 Bird
Density (cov) p0.01
rmANCOVA Compound Symmetry Log-transformed Year
p lt 0.0001 Ecotype p0.10 Bird Density (cov)
p0.02
y 0.031x 0.34 r2 0.0332
y 0.023x 0.11 r2 0.0202
0.8
0.8
Herbivore Abundance (residuals)
Herbivore Abundance (residuals)
0
0
-0.8
-0.8
30
0
30
0
15
15
Birds w/in 200m
Birds w/in 200m
27
Effect of Bird Density on Herbivore Abundance
rmANCOVA Unstructured Square-root
transformed Year p lt 0.0001 Ecotype
p0.728 Bird Density (cov) p0.430
Pre-treatment (1993-1995)
rmANCOVA First Order Autoregressive Log-transforme
d Year p lt 0.0001 Ecotype p0.056 Treatment
p0.311 Bird Density (cov) p0.061
Post-treatment (1997-2000)
y -0.0015x 0.0134 r2 0.0022
2.0
0.6
Herbivore Abundance (residuals)
Herbivore Abundance (residuals)
0
0
-1.5
-0.5
30
0
30
0
15
15
Birds w/in 200m
Birds w/in 200m
28
Effect of Bird Density on Free Feeder Herbivore
Abundance
rmANCOVA First Order Autoregressive Log-transforme
d Year p lt 0.0001 Ecotype p0.001 Bird Density
(cov) p0.067
rmANCOVA Compound Symmetry Log-transformed Year
p lt 0.0001 Ecotype p0.120 Treatment
p0.360 Bird Density (cov) p0.026
Pre-treatment (1993-1995)
Post-treatment (1997-2000)
y -0.0058x 0.0527 r2 0.0210
y -0.0066x 0.0651 r2 0.0223
0.8
0.8
Free Feeder Abundance (residuals)
Free Feeder Abundance (residuals)
0
0
-0.8
-0.8
30
0
30
0
15
15
Birds w/in 200m
Birds w/in 200m
29
Effect of Bird Density on Ratio of Free Feeders
to Shelter Builders
rmANCOVA First Order Autoregressive Log-transforme
d Year p 0.708 Ecotype p lt0.0001 Bird Density
(cov) p0.043 Bird Density Year 0.001
Pre-treatment (1993-1995)
y -0.0107x 0.1064 r2 0.0473
0.8
Ratio free feeders to shelter builders (residuals)
0
-0.8
30
0
15
Birds w/in 200m
30
Effect of Bird Density on Ratio of Free Feeders
to Shelter Builders
rmANCOVA Compound Symmetry Log-transformed Year
p lt 0.0001 Ecotype p0.015 Treatment
p0.229 Bird Density (cov) p0.011 Bird Density
Year 0.0004
Post-treatment (1997-2000)
y -0.0059x 0.0536 r2 0.0214
0.8
Ratio free feeders to shelter builders (residuals)
0
-0.8
30
0
15
Birds w/in 200m
31
Preliminary Conclusions
  • All herbivores considered together
  • no relationship between insects and birds
  • Just free feeders
  • Some evidence for negative correlation between
    insects and birds
  • Ratio of free feeders to shelter builders
  • Birds shift herbivore community structure in some
    years but not others

32
Refining the Model
  • Under construction

33
Territory From Point to Area
  • A challenge
  • Preliminary analysis crude
  • Conspecifics defend territories
  • Territory size may depend on
  • Bird species
  • Topography
  • Region (i.e. Ozark highlands)
  • Year
  • Territories may not be circular

center of territory modeled
territory
34
Territory From Point to Area
  • Euclidean polygons
  • ½ distance to nearest conspecific in 360 degrees
  • Maximum
  • mean distance to nearest conspecific/2 1 SD
  • Limit territory by topography

35
Insect Stand From Point to Distribution
  • Stands distributed in space
  • Stand as point can be
  • inaccurate
  • misleading
  • Abundance best by stand
  • Predation pressure
  • per tree
  • summed across trees to stand

36
Diet and Foraging
37
Summary
  • Preliminary evidence for top-down effects of
    birds on insects
  • Working with authors to make the model more
    biologically relevant
  • Territory size
  • Diet and foraging behaviors

38
Acknowledgments
Kathleen Baker Herbivore crews Bird crews Randy
Jensen Missouri Department of Conservation Marquis
Lab
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