Use of Assisted Migration and Community Zonation Patterns ......Use of Assisted Migration and...
Transcript of Use of Assisted Migration and Community Zonation Patterns ......Use of Assisted Migration and...
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Use of Assisted Migration and Community Zonation Patterns to Build a Climate-
Resilient Coastal Landscape
Loretta L. Battaglia Hannah J. Kalk
Southern Illinois University
Carbondale, Illinois USA
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Coastal plant communities and altered inundation regimes
Adapt, go extinct, or migrate inland
Credit: wetlandextension.ifas.ufl.edu
With only 1 m rise in sea-level, 26-66% of coastal wetlands will be lost (Mitsch and Gosselink, 2007)
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Climate Change and Restoration
• “Moving targets”
– Rate of change
– Direction of change
• Anticipatory or futuristic restoration
• Assisted migration
Time
Envi
ron
me
nta
l Var
iab
le
LinearExponential
Time
Envi
ron
me
nta
l Var
iab
le
Fast
Slow
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Relative Ease of Futuristic Restoration
Rate of Change
Slow Fast
Pattern of
Spatial
Change
Linear High Moderate
Exponential Moderate Low
Erratic or
No-analogue ? ??
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Coastal Wetlands
• Spatial zonation of communities along strong environmental gradients
• Stress-tolerant species at seaward end, stronger competitors farther inland (Bertness and Ellison 1987, Pennings et al.
1995)
• Rate of change varies depending on relative SLR, etc.
• N. Atlantic, Gulf of Mexico, especially at risk (Hammer-Klose and Thieler 2001, Meehl et al. 2005, Ramstorf 2007)
National Geographic
Loretta Battaglia
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Relative Ease of Futuristic Restoration
Rate of Change
Slow Fast
Direction of
Spatial
Change
Linear High Moderate
Non-linear Moderate Low
Erratic or
No-analogue ? ??
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Study Questions
• With removal of biotic filters, can dominant species from seaward communities establish and survive when introduced into landward locations? (Reciprocal planting study – Weeks Bay, AL)
• Can assisted colonization enable successful futuristic restoration and if so, how futuristic? (FEMA Restoration Sites – Grand Bay, AL)
Gulf of Mexico
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Northern Gulf of Mexico
• Relatively slow relative SLR
Weeks Bay NERR
Gulf of Mexico
Grand Bay NERR
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Dominants of Seaward Vegetation Zones
• Salt marsh: Spartina alterniflora
• Brackish marsh: Juncus roemerianus
• Fresh marsh: Cladium jamaicense
Weeks Bay NERR
Gulf of Mexico
Open Water Salt Marsh Fresh
Marsh
Terrestrial
Forest Forest-
Marsh
Ecotone Brackish
Marsh
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Methods
• Late Summer 2008 vegetation removed in 1m2 plots
• Five culms of 3 dominant species from 3 most seaward vegetation zones planted in monoculture
• Transplant zones (3 sp x 5 reps; total plots = 75) – Salt marsh (SM) – Brackish marsh (BM) – Fresh marsh (FM) – Fresh marsh – Forest ecotone (EC) – Wetland seep forest (FO)
• Survival (and growth) monitored seasonally for 2 years
Weeks Bay NERR
seaward
landward
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Removal of Standing Vegetation
Weeks Bay NERR
Gulf of Mexico
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Planting of Culms
Weeks Bay NERR
Gulf of Mexico
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Results
Weeks Bay NERR
Gulf of Mexico
SM BM FM EC FO
Per
cen
t Su
rviv
al
0.0
0.2
0.4
0.6
0.8
1.0
a
ab
b b b
SM BM FM EC FO
Per
cen
t Su
rviv
al
0.0
0.2
0.4
0.6
0.8
1.0
SM BM FM EC FO
Per
cen
t Su
rviv
al
0.0
0.2
0.4
0.6
0.8
1.0
Spartina Juncus
Cladium
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Summary of Results
• All species established and survived in at least one of the zones landward of their original zone
• Juncus exhibited the broadest “new” distribution – Established seaward of original position
– Thriving in forest (canopy openings from Hurricane Katrina in 2005)
• Cladium was able to establish landward as well, but not in more seaward zones
Weeks Bay NERR
Gulf of Mexico
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FEMA Buyout Homestead Sites • 15 former pine forests adjacent to GBNERR
• Purchases began following inundation by
Hurricanes Georges in 1998
• Highly disturbed
• Heavily infested with noxious exotics: Imperata cylindrica , Panicum repens and Triadica sebifera
• Vacant and awaiting management
Credit: L. Battaglia
Credit: L. Battaglia
Credit: L. Battaglia
Credit: MDMR
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Design of Propagule Bank Experiment Randomly Selected: 5 sites, 9m X 13m plots, 24- 1m X 1m subplots
S B F M W C
M F C C B B
F M W S W C
S M W B F W
Site Preparation: herbicide, mowing, tilling, raking
Legend S: Salt marsh B: Brackish marsh F: Freshwater marsh M: Maritime pine island W: Wet pine flatwood C: Control
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Donor Bank Collection and Application 0.50m x 0.25 m sods
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Data Collection and Site Maintenance
•Presence/Absence data •Species removed: Eupatorium capillifolium, Centrosema virginiana, Ipomoea quamoclit and Cuphea glutinosa
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Richness and Diversity
• Site preparation greatly increased species richness and diversity
• Highest in plots with freshwater sods, relative to plots with control and saline marsh sods
Propagule sod treatment
U C S B F MP PF
Mea
n s
pec
ies
rich
nes
s
0
5
10
15
20
25
30
a
ab
ab
b bb
Propagule sod treatment U C S B F MP PF
Me
an
sp
eci
es
div
ers
ity
(H
')
0.0
0.5
1.0
1.5
2.0
2.5
3.0
3.5
ab
ab abbb
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Axi
s 3
Axis 1A
xis
2
Compositional Trends
Stress value= 0.17, based on absence/presence data
Site 1: Brackish Marsh
Site 1: Control
Site 1: Freshwater Marsh
Site 1: Maritime Pine
Site 1: Pine Savanna
Site 1: Salt Marsh
Site 2: Brackish Marsh
Site 2: Control
Site 2: Freshwater Marsh
Site 2: Maritime Pine
Site 2: Pine Savanna
Site 2: Salt Marsh
Site 3: Brackish Marsh
Site 3: Control
Site 3: Freshwater Marsh
Site 3: Maritime Pine
Site 3: Pine Savanna
Site 3: Salt Marsh
Site 4: Brackish Marsh
Site 4: Control
Site 4: Freshwater Marsh
Site 4: Maritime Pine
Site 4: Pine Savanna
Site 4: Salt Marsh
Site 5: Brackish Marsh
Site 5: Control
Site 5: Freshwater Marsh
Site 5: Maritime Pine
Site 5: Pine Savanna
Site 5: Salt Marsh
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Effects of Site on Composition
• PERMANOVA: Pseudo-F = 31.05, p < 0.0010
% Sand % Silt % Clay Mean % Soil Moisture Salinity (ppt) Conductivity(µs/cm)
Site 1 69.8 19.6 10.6 28.3 0.3 568.0
Site 2 63.8 23.6 12.6 40.0 0.1 199.2
Site 3 62.4 29.6 8.0 29.2 0.2 388.5
Site 4 66.4 25.0 8.6 33.5 0.1 221.1
Site 5 56.5 30.9 12.6 24.3 0.2 442.9
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Effects of Propagule Sod on Composition
• PERMANOVA: Pseudo-F = 3.06, p < 0.0010
Control Salt marsh Brackish marsh Fresh marsh Maritime pine island
Salt marsh 0.001
Brackish marsh 0.104 0.081
Fresh marsh 0.001 0.001 0.001
Maritime pine island 0.001 0.001 0.001 0.105
Pine savanna 0.008 0.008 0.007 0.001 0.001
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Recruitment of Target Species • Targets emerge both from seed and resprout, most are indicator species
from seed bank assessment
Vegetation Zone Total # of Target
Species
Most Abundant Species % of Subplots (Across
all 5 sites)
Salt Marsh 2 Spartina alterniflora 15
Distichlis spicata 5
Brackish Marsh 1 Juncus roemerianus 40
Freshwater Marsh 5 Sabatia stellaris 45
Panicum virgatum 15
Maritime Pine Island 6 Spartina patens 85
Pinus elliottii 20
Scirpus lineatus 15
Wet Pine Flatwood 17 Aristida beyrichiana 45
Andropogon glomeratus 35
Lachnanthes caroliniana 30
Aletris lutea 20
Lycopodiella prostrata 15
Sarracenia alata 5
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Distribution of Desirable Taxa
• Mean number of taxa in each functional category varies significantly across sod treatment types and sites
• More target species in freshwater and wet pine flatwood plots than in control and salt marsh plots
Sod treatment typeC S B F MP PF
Mea
n #
of
taxa
/plo
t
0
5
10
15
20Generalist Species
Alien Species
Target Species
Noxious Species
a a a a aa
a b aba ab ab
cc
bc
aab
aa a
a
a
a a
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• Species diversity and richness increased, and noxious species greatly reduced on all treated areas
• Propagule sods resulted in “hybrid” communities (Hobbs et al. 2009),
containing generalist and alien species, as well as indicator species from historic communities
• A viable propagule source for restorations, containing taxa with diverse life histories and environmental tolerances (Pywell et al. 1995, Brown and Bedford 1997, Anderson and Cowell 2004)
• Freshwater marsh and maritime pine island sods best suited to the restoration sites – seaward species can tolerate inland conditions
• Local environmental conditions and proximity to ruderal source populations also drive community composition/dynamics
Summary of Results
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Is anticipatory restoration feasible?
• Yes, but… – Differing degrees depending on species and background
environmental change – Short-term success of propagule bank application in instilling
diverse species into degraded ecosystems, long-term storage important
• Rate and direction of underlying abiotic change are key drivers – Communities that are sequentially arranged along strong
environmental gradients may be easiest – Lack of spatial contiguity may require assisted colonization – Exotic species
• Use of common futuristic garden experiments at natural ecotones in the landscape to ease transition for vulnerable communities and enhance landscape fluidity (Manning et al. 2009) as climate change and sea-level rise alter site conditions
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Acknowledgements
• Brooks Davey
• Jeni Miller
• Scott Phipps
• Scott Schuette
• Joey Weber
Gulf of Mexico
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Questions?
Weeks Bay NERR
Gulf of Mexico
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Vegetation-Seedbank Comparison
• Procrustes RMS Residual (mean distance between parent vegetation and SB, goodness of fit)
Axis 1
-3.0-2.5-2.0-1.5-1.0-0.50.00.51.01.52.0
Axi
s 2
-1.0
-0.5
0.0
0.5
1.0
1.5
V SM
V LB
V UB
V FM
V MPI
V WPF
S SM
S LB
S UB
S FM
S MPI
S WPF
Procrustes RMS Residual =0.5559