HABITAT SUSCEPTIBILITY TO INVASION BY COGONGRASS ON CAMP SHELBY TRAINING SITE, MS - PowerPoint PPT Presentation

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HABITAT SUSCEPTIBILITY TO INVASION BY COGONGRASS ON CAMP SHELBY TRAINING SITE, MS

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Degrades Gopher Tortoise Habitat. Alters Fire Intensity and Frequency. Why Do We Care? ... gopher tortoise habitat. longleaf pine/bluestem habitat ... – PowerPoint PPT presentation

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Title: HABITAT SUSCEPTIBILITY TO INVASION BY COGONGRASS ON CAMP SHELBY TRAINING SITE, MS


1
HABITAT SUSCEPTIBILITY TO INVASION BY COGONGRASS
ON CAMP SHELBY TRAINING SITE, MS
Lisa Y. Yager, The Nature Conservancy Deborah L.
Miller, University of Florida Jeanne Jones,
Mississippi State University
2
Cogongrass
  • Spread by wind-dispersed seeds, man-dispersed
    rhizomes, rhizomatous growth.
  • Establishes in a wide variety of habitats
    including roadsides, firing points, upland pine
    forests, and wetlands

3
Why Do We Care?
  • Displaces Native Species

4
Why Do We Care?
  • Poor Forage Quality
  • Degrades Gopher Tortoise Habitat

5
Why Do We Care?
  • More Flammable, Burns Hotter
  • Alters Fire Intensity and Frequency

6
Camp Shelby Training Site
7
(No Transcript)
8
Limited Resources
  • Protect and prioritize areas of high conservation
    value
  • gopher tortoise habitat
  • longleaf pine/bluestem habitat
  • Determine most effective use of resources for
    prevention and control

9
Objectives
  • Compare
  • Linear Vegetative Growth
  • Seed Dispersal
  • In Different Habitats

10
Pine/Bluestem
Pine/Shrub
11
Hardwood
Mowed Herbaceous
12
Vegetative Growth- Methods
13
Vegetative Growth 2003
Mean
Maximum
4
3.22
3.5
2.72
3
2.57
2.53
2.5
Tiller Extension (m/yr)
1.89
2
1.5
1.09
0.92
0.85
1
0.6
0.56
0.5
0
Hardwood
Pine/
Pine/
Roadside
Military
Bluestem
Shrub
Areas
14
Vegetative Growth 2004
6
5.0
Mean
Maximum
5
4
3.49
Tiller Extension (m/yr)
3
2.36
2.16
1.92
2
0.91
0.78
0.74
0.71
1
0.48
0
Hardwood
Pine/
Pine/
Roadside
Military
Bluestem
Shrub
Areas
15
Soil Disturbance
  • Military Training Areas
  • Patches with gt 7 m and gt 10 m linear growth
  • Reduced patch size for 2003 and 2004 for a patch
    which was rehabilitated- disked and planted
    with ryegrass

16
Seed Dispersal
  • 3 Locations for Each Habitat
  • 5 Releases of 50 Spikelets/ Habitat/ Location
  • Flag and GPS Locations

17
Mean Maximum Wind Speed
Pine/Bluestem
1.7 m/sec
Pine/Shrub
0.7 m/sec
18
Seed Dispersal
40
40
35
35
Pine/Bluestem
Pine/Bluestem
Pine/Shrub
Pine/Shrub
30
30
n 15
25
25
20
20
Dispersal Distance (m)
15
15
10
10
5
5
0
0
Mean Distance
Maximum Recordable Distance
19
Seed Dispersal
30
30
Pine/Bluestem
Pine/Bluestem
25
25
Pine/Shrub
Pine/Shrub
Spikelets
20
20
15
15
Percentage of
10
10
5
5
0
0
gt 5 m
gt 5 m
gt 10 m
Distance Dispersed
20
Seedbed
  • Spikelets Landing on Bare Ground or Litter
  • Pine/Bluestem Pine/Shrub

34
16
21
Conclusion
  • Vegetative encroachment by cogongrass occurred in
    all habitat types
  • Cogongrass vegetative growth rate was lowest into
    the hardwood habitat

22
Conclusion
  • Soil disturbance can enhance rapid vegetative
    growth

23
Conclusions
  • Cogongrass spikelets penetrated further into the
    pine/bluestem habitat type
  • Cogongrass spikelets were more likely to land on
    bareground or litter in the pine/bluestem habitat

24
Priorities
  • Pine/bluestem and Military Training Areas (Mowed
    Herbaceous Habitats)
  • Treatment of cogongrass prior to activities which
    create soil disturbance or reduce canopy/shrub
    cover

25
Acknowledgements MS Army National Guard USDA
Forest Service The Nature Conservancy Brian
Mitchell, Robin Switzer, CJ Sabette, Jeff
Kaminski.
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