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Bambi

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Loss of American chestnut. Regional failed oak and hickory regeneration. Massive clear-cutting ... Chestnut and chestnut blight. Beech and beech bark disease ... – PowerPoint PPT presentation

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Title: Bambi


1
Bambi Smokey Bear New Realities for Forest
Management in the 21st Century
Walter Carson1, Henry Schumacher1, Rachel
Collins2, Mary Beth Adams3 1University of
Pittsburgh, 2Univ Wisconsin, 3USFS NE Forest
Research Station
2
Final Exam Wed. Dec. 13, 12-150 in A224 Langley
Hall This room
  • Dramatic shifts in tree species composition in
    eastern deciduous forests over the past 100
    years.
  • Loss of American chestnut
  • Regional failed oak and hickory regeneration
  • Massive clear-cutting
  • Rise of the Swamp Thing
  • Current loss of American beech

3
Introduction to the problem
  • Shifts in composition have coincided with
  • A century of fire suppression (Smokey Bear)
  • Increased deer populations (Bambi)
  • Alteration of canopy gap dynamics (Clear-cutting)

4
Research questions
  • What ecological processes (e.g. light, deer,
    fire) have caused these changes in species
    composition?
  • Does one process drive the patterns, or does more
    than one process interact to drive these changes?
  • The Deer Camp vs. The Fire Camp.

5
3 general conceptual models of forest
regeneration dynamics
  • Shade Tolerance Model (STM)
  • Mammalian Browsing Model (MBM)
  • Fire Tolerance Model (FTM)

6
Shade tolerance model (STM)
  • As disturbance severity increases, absolute and
    relative abundance of shade-intolerant species
    increases.
  • Light is the most limiting resource in
    understory
  • Species shade tolerance drives regeneration

7
Shade Tolerance Model
  • Species have different life-history strategies.
  • Trade-off between high-light growth and low-light
    survival (shade tolerance)
  • Physiological constraints prevent super-species

Kobe et al. 1995
8
Shade Tolerance Model
  • Shade tolerant species
  • American beech, sugar maple, hemlock
  • Intermediate shade tolerant species
  • Oaks, hickories, red maple, black cherry
  • Shade intolerant species
  • Yellow/Black birch, Pin cherry, Tulip poplar,
    Aspen

9
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10
Mammalian browsing model (MBM)
  • Pre- and post-disturbance communities will be
    composed of browse-tolerant species.
  • Assumes that mammalian browsers have a major
    impact on species composition, over the past and
    now.

11
Deer populations are much higher than historic
estimates
1500 A.D. 3.5 Deer km-1 McCabe McCabe
(1997) Todays densities 3 deer km-1 6 deer
km-1 12 deer km-1 gt18 deer km-1
www.qdma.com
12
Mammalian Browsing Model
  • High deer abundances lead to an understory of
    browse-tolerant species.
  • Deer prevent browse-intolerant species from
    regenerating.
  • Browse-tolerance may interact with shade-tolerance

13
Hay-scented Fern in Allegheny National Forest
14
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15
High plant diversity only found on refugia
BOULDERS!!
16
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17
Fire Tolerance Model (FTM)
  • Fire increases the absolute and relative
    abundance of fire-tolerant species and decrease
    the abundance of fire-intolerant species

18
Fire Tolerance Model
  • Natural anthropogenic fires common for 1000s of
    years
  • Re-occurring fires should promote fire tolerant
    species
  • Fire-tolerant species have adaptations to fire

19
Fire Tolerance Model
  • Fire and oak hypothesis
  • Abrams (1992, 2003)
  • Oak abundance and fire frequency correlated
    (gt7,000 yrs)
  • Delcourt Delcourt (1987)

20
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21
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22
Lightning strike density (per sq.km/yr)
Lightning storms rare in west, common in southeast
23
Forest Dynamics Project, WV
  • Investigate the individual and interactive
    effects of
  • Light availability
  • Deer browsing
  • Understory fire

24
Study Sites
  • 2 sites in West Virginia
  • MeadWestvaco Research Forest
  • Dominated by sugar maple
  • 10-20 oak canopy
  • 17 deer km-1 (4x)
  • USFS Fernow Forest
  • Oak dominated
  • 8 deer km-1 (2x)

USFS Fernow
MeadWestvaco Research Forest
25
Treatment layout in each Stand (40 ha)
16 research plots per stand
Fire
No Fire
20m x 20m subplot
canopy gap
fence
plot
26
Data collected
  • Censuses
  • 1997 (pre-treatment)
  • 1999, 2000, 2004 (post-treatment)
  • gt20,000 individuals tagged at each site
  • Definitions
  • Canopy (gt10cm DBH)
  • Saplings (1-10cm DBH)
  • Seedlings (20-140cm Height)

27
Density Deer mask the effects of disturbance
28
Density Deer mask the effects of disturbance
72 pioneers
81 pioneers
29
Density by species Are species compositions
changing?
30
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31
STM As disturbance severity increases, absolute
and relative abundance of shade-intolerant
species increases.
  • STM supported in the ABSENCE of deer.
  • Gaps shifted species compositions only when deer
    were absent.

32
MBM Pre- and post-disturbance communities will
be composed of browse-tolerant species.
  • In presence of deer, MBM made most accurate
    predictions.
  • Deer disproportionately reduced shade intolerant
    species especially in gap fire treatments.

33
FTM Fire will increase the absolute and relative
abundance of fire-tolerant species and decrease
the abundance of fire-intolerant species
  • Fire-tolerant species did not increase in
    relative abundance after fires.
  • Deer control the species composition following
    fire.
  • Fire shifted species compositions only when deer
    were absent.

34
Deer mask the effects of gaps fire
Fire Gap without deer browsing
Fire Gap with deer browsing
35
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36
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37
Are we going to lose the major masting species
in the Eastern Deciduous forest
  • Chestnut and chestnut blight
  • Beech and beech bark disease
  • Oaks and hickories (fire and deer)

38
Acknowledgements
  • MeadWestVaco Corp.
  • Pat Keyser, Vic Ford, Bruce Brenneman
  • USDA Forest Service
  • Tom Schuler, Mark Ford, Gary Bustemente, Gary
    Willison, Tim Sherm
  • University of Pittsburgh
  • EE Grad Student Community Faculty
  • Funding
  • USDA Forest Service, USDA NRI, Phipps
    Conservatory, Garden Club of Allegheny County,
    Mead-Westvaco, Babcock Charitable Trust
  • Field Workers
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