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Marsh terracing as a restoration technique for creating nekton habitat

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USGS Louisiana Cooperative Fish and Wildlife Research Unit ... Clown goby. Unterraced. Terraced. NSD. Rainwater killifish. Western mosquitofish. Naked goby ... – PowerPoint PPT presentation

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Title: Marsh terracing as a restoration technique for creating nekton habitat


1
Marsh terracing as a restoration technique for
creating nekton habitat
  • USGS Louisiana Cooperative Fish and Wildlife
    Research Unit
  • School of Renewable Natural Resources
  • Louisiana State University Agricultural Center
  • Baton Rouge, LA

2
COASTAL RESTORATION
  • To restore and increase vegetated marsh and
    submerged aquatic vegetation habitat in terms of
    both quantity and quality
  • To increase fishery habitat in terms of area and
    quality

3
Field of dreams hypothesis if you build it,
they will come
4
MEASURING SUCCESS
  • Area of vegetated marsh created
  • Establishment of marsh vegetation
  • Functional equivalency
  • Habitat quality (density, standing stock)
  • Habitat suitability (species occurrence)
  • Food chain support (diet)
  • Fitness (condition or growth)

5
OBJECTIVES
  • Determine the effect of marsh terraces on
    adjacent water quality and sediment
    characteristics.
  • Compare nekton communities in paired terraced and
    unterraced ponds
  • Density (habitat quality)
  • Community assemblages (habitat suitability)
  • Condition (fitness)

6
PREVIOUS TERRACE RESEARCH
  • Rozas and Minello 2001
  • Maximize marsh edge
  • Bush Thom et al. 2004
  • Differences in community composition

7
STUDY SITES
  • Three sets of paired terraced and unterraced
    ponds (Rockefeller SWR (Sites 1 2) Sabine NWR
    (Site 3)).
  • Sampling at three habitat types
  • 1) terraced marsh edge
  • 2) unterraced marsh edge
  • 3) open water
  • Sampled 7 times
  • bi-monthly April 2004 April 2005
  • 7 sample dates x 3 sites x 2 ponds x 4 sites
    168 samples

8
  • Terraced Pond
  • Two terraced edge (lt 1m)
  • Two open water (gt 50 m edge)

9
  • Unterraced Pond
  • Two unterraced edge (lt 1m)
  • Two open water (gt 50 m)

10
METHODS
  • Nekton
  • Samples were collected with a 1-m2 throw trap. A
    bar seine is used to clear all nekton from the
    trap.

11
METHODS
  • Water Quality Soils
  • Depth and water quality data (salinity,
    conductivity, temp., D.O., turbidity) were
    collected along with each nekton sample.
  • Percent organic matter
  • SAV
  • All submerged aquatic vegetation was collected
    from the throw trap.

12
STATISTICAL ANALYSES
  • Habitat quality
  • Compare water quality, nekton density, biomass,
    richness and diversity between terraced and
    unterraced edge and open water sites (ANOVA)
  • Habitat Suitability
  • Compare species composition (Chi-square)
  • Nekton Condition
  • Compare dominant species length-weight
    relationships (ANCOVA)

13
RESULTS ENVIRONMENTAL CHARACTERISTICS
  • Turbidity (P 0.23)
  • lower in terraced ponds
  • SAV (P lt 0.0001)
  • higher biomass in terraced ponds
  • Soil Organic Matter (P 0.003)
  • lower at terraced edge

14
FUNCTIONAL EQUIVALENCY TRAJECTORY
Craft et al. 2003
15
45
40
35
30
25
Nekton Density (individuals/m2)
20
15
10
5
0
Edge
Open water
Edge
Open water
Terraced
Unterraced
Habitat Type
16
45
A
40
35
B
30
25
Nekton Density (individuals/m2)
20
15
10
5
0
Edge
Open water
Edge
Open water
Terraced
Unterraced
Habitat Type
17
A
45
A
40
35
30
25
Nekton Density (individuals/m2)
20
15
10
5
0
Edge
Open water
Edge
Open water
Terraced
Unterraced
Habitat Type
18
CONCLUSIONS
  • Habitat characteristics differed between terraced
    and unterraced ponds (SAV, organic matter,
    turbidity).
  • Habitat quality, as measured by nekton density
    and diversity, were similar between terraced and
    unterraced edges.

19
NEKTON SPECIES COMPOSITION
Daggerblade grass shrimp
Rainwater killifish
Inland silverside
Sailfin molly
Naked goby
Blue crab
Western mosquitofish
Other
n 1,623
n 1,921
20
Chi-sq P lt 0.0001
21
CONCLUSIONS
  • Habitat characteristics differed between terraced
    and unterraced ponds (SAV, organic matter,
    turbidity).
  • Habitat quality, as measured by nekton density
    and diversity were similar between terraced and
    unterraced edges.
  • Habitat suitability, as measured by species
    abundances and community composition, differed
    significantly between terraced and unterraced
    habitats with greater proportion of benthic
    dependent species at unterraced edge, and
    greater proportions of pelagic species in
    terraced habitats.

22
FISH CONDITION
  • Based on length / weight relationship
  • Heavier fish better condition

Lucania parva
0.0
log10(W) a' b log10(L)
-0.5
W' aLb
Kn W / W'
log10(weight)
-1.0
-1.5
-2.0
0.0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
log10(length)
23
Cyprinodon variegatus ANCOVA
terraced
unterraced
24
Condition (length-weight)
Terraced
Unterraced
NSD
  • Inland silverside
  • Sheepshead minnow
  • Clown goby
  • Rainwater killifish
  • Western mosquitofish
  • Naked goby
  • Sailfin molly

25
CONCLUSIONS
  • Habitat characteristics differed between terraced
    and unterraced ponds (SAV, organic matter,
    turbidity).
  • Habitat quality, as measured by nekton density
    was similar between terraced and unterraced
    edges.
  • Habitat suitability, as measured by species
    abundances and community composition, differed
    significantly between terraced and unterraced
    habitats.
  • Nekton fitness or health, as measured by length
    weight relationships, was lower in terraced as
    compared to unterraced ponds for 3 species, and
    similar between terraced and unterraced ponds
    for 3 different species.

26
FUNCTIONAL EQUIVALENCY TRAJECTORY
(Hobbs and Mooney 1993)
Restoration
Alternative states
Complexity / function
Stays the same
Continued decline
Time
Plant biomass (3-5 yrs) benthic communities
(10-15 yrs) soil properties (30 years) (Craft
et al. 1999, Craft 2003, Broome et al. 1986)
27
FUNCTIONAL EQUIVALENCY
  • Terraces do provide nekton habitat, largely
    through the provision of edge habitat.
  • However, ecological equivalency is clearly not
    achieved within 4 years of restoration (as
    measured in this project).
  • Species occurrence or abundance only provide a
    part of the picture - measures of species health
    and community assemblages need to be considered
    to fully capture the value of restored marshes.

28
  • Funding provided by CREST (Coastal Restoration
    and Enhancement through Science and Technology)
  • Thanks to Rockefeller SWR and Sabine NWR for
    access to sites, and logistical help.
  • Thanks to Chris Cannaday, Jessica OConnell,
    Bryan Piazza, Tim Birdsong, and Seth Bordelon for
    assistance in the field.
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