Site-Specific Habitat and Landscape Associations

Transcription

Site-Specific Habitat and Landscape Associations
Site-specific habitat and landscape
associations of Rusty Blackbirds wintering
in Louisiana
Sinéad M. Borchert and Philip C Stouffer
School of Renewable Natural Resources
Louisiana State University
Stouffer Lab
Emma DeLeon
Angelica Hernandez-Palma
Erik Johnson
Karl Mokross
Luke Powell
Cameron Rutt
Jared Wolfe
Committee Members
Dr. Michael Kaller
Dr. Sammy King
Rusty Blackbird Working Group
Student Workers
Jamie Amato
Collins Fairley
Kelsey Koppelberger
Amber Moses
Cover photo by Erik Breden
Funding:
Lucius W. Gilbert Foundation and the
LSU School of Renewable Natural Resources
Field Support
Samantha Lantz
Matt Brady
Billy Watson
Jim Boyce
Harrold Quave
Ryan Lemoine, Paul, Johnny Warren – Yancey WMA
Joe Neurig, LSUAgCenter Lee Forest
Denise McKinney, Bogue Chitto SP
Mark Simon, ULL Experimental Farm
Longfellow-Evangeline State Historic Site
Lake Fausse Pointe SP
Fairview Riverside SP
Fontainebleau SP
Sherburne WMA
Town of Grosse Tete
LABIRD list-serve members
Analysis Advice
Maurice Wolcott
Kristin Brzeski

Ground forager

“Forested wetland
specialist”
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Shallow water, wet
leaf litter, grass
important variables
(DeLeon 2012)
Dr. Geoffrey Hill
3
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Emma DeLeon
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Emma DeLeon
0
2011
2009
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birds/party hour
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Courtesy of Emma DeLeon
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80% of bottomland hardwood
forests converted to
agriculture
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Mississippi Alluvial Valley
 57% wetland loss
 25% of floodplain forested
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1950s-1960s hydrological
change
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Determine habitat needs using site (100 m)
and landscape scale (600 m) variables
Erik Breden
Bill Hilton Jr.
SE Louisiana, USA
68 sites total
57 sites year 2
534 surveys total
≥ 1200 m apart
Surveys
100 m
200 m
200 m point count
100 m ground cover
habitat survey
600 m Landscape Scale
land cover
30 m resolution
GAP data
reclassified using
International Rusty
Blackbird Working
Group classes
soils
SSURGO data
4 major hydrologic groupings
600 m Landscape Scale
rainfall
PRISM precipitation data
4 km resolution
Average rainfall 3 days
prior to survey period
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3 repeated surveys within
a season
4 day closure period
(most completed within 3
consecutive days)
Site
1
2
3
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Package unmarked for R
Model detectability (p) with
occupancy (Ψ )
Model how habitat covariates
affect Rusty Blackbird presence
at a site
Site
1
2
3
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air moisture (sunny to rain 1-4)
Beaufort wind speed (1-5)
prior detection
other blackbirds (flock size)
Common Grackles
Red-winged Blackbirds
open space (grass cover)
Most important:
Common Grackles + open space + prior detection
site % ground cover (100 m):
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shallow water (≤ 5 cm)
wet leaf litter
leaf litter
wet grass
woody debris
Mike Tracy
landscape % cover (600 m):
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floodplain forest
woody wetland
developed
agriculture
rainfall
soil hydrologic group C
soil hydrologic group D
Model P(COGR + open + prior)
ΔAIC
weight
k
0
0.18
7
Ψ(woody wetland + wet litter)
0.23
0.16
7
Ψ(wet litter)
1.03
0.11
6
4.42
0.02
13
10.62
0.00
2
Ψ(wet litter + wet grass)
Ψ(global)
Ψ(null)
Model P(COGR + open + prior)
Ψ(wet litter + wet grass)
ΔAIC
weight
k
0
0.18
7
0.16
7
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wet leaf litter + (site scale)
wet grass + (site scale)
Ψ(woody wetland + wet litter)
0.23
Ψ(wet litter)
 woody0.11
wetland6– (landscape scale)
1.03
Ψ(global)
(but overall positive when with
wet leaf litter)
4.42
0.02
13
Ψ(null)
10.62
0.00
2
Ψ(wet litter + wet grass)
(t₀ = 24.5, α = 0.05, p = 0.18)
Ψ(woody wetland + wet litter) (t₀ = 25.1, α = 0.05, p = 0.18)
Ψ(wet litter)
All top models had good fit
(parametric bootstrap method)
(t₀ = 25.4, α = 0.05, p = 0.36)
Model averaged occupancy:
0.50 ± 0.23 (SD)
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Top model: presence of wet leaf litter and wet grass
at a site
 site-level substrate more important than land cover?
Jeff Trahan
Jeff Trahan

Wet leaf litter and woody wetland had an overall
positive effect on occupancy
 woody wetland class = baldcypress (Taxodium distichum)
tupelo (Nyssa aquatica) swamp
 wet leaf litter = shallow swamps
 shallow swamp > deep swamp
What does this mean for Rusty
Blackbird habitat
management in Louisiana?
- Diversions
- Low water (timing & frequency)
- Tree buffers around swamps

Dynamic N-mixture
(abundance) modeling
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Invertebrate biomass
estimate as a measure of
food availability
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Landscape variables at
the 6 km scale

Louisiana Winter Bird
Atlas landscape analysis
Questions?
Erik Breden
Naïve Detection probability: 0.65 ± 0.07
Naïve Occupancy probability: 0.37 ± 0.07

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