Title: Marsh terracing as a restoration technique for creating nekton habitat
1Marsh 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
2COASTAL 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
3Field of dreams hypothesis if you build it,
they will come
4MEASURING 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)
5OBJECTIVES
- 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)
6PREVIOUS TERRACE RESEARCH
- Rozas and Minello 2001
- Maximize marsh edge
- Bush Thom et al. 2004
- Differences in community composition
7STUDY 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)
10METHODS
- Nekton
- Samples were collected with a 1-m2 throw trap. A
bar seine is used to clear all nekton from the
trap.
11METHODS
- 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.
12STATISTICAL 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)
13RESULTS 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
14FUNCTIONAL EQUIVALENCY TRAJECTORY
Craft et al. 2003
1545
40
35
30
25
Nekton Density (individuals/m2)
20
15
10
5
0
Edge
Open water
Edge
Open water
Terraced
Unterraced
Habitat Type
1645
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
17A
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
18CONCLUSIONS
- 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.
19NEKTON SPECIES COMPOSITION
Daggerblade grass shrimp
Rainwater killifish
Inland silverside
Sailfin molly
Naked goby
Blue crab
Western mosquitofish
Other
n 1,623
n 1,921
20Chi-sq P lt 0.0001
21CONCLUSIONS
- 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.
22FISH 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)
23Cyprinodon variegatus ANCOVA
terraced
unterraced
24Condition (length-weight)
Terraced
Unterraced
NSD
- Inland silverside
- Sheepshead minnow
- Clown goby
- Rainwater killifish
- Western mosquitofish
- Naked goby
25CONCLUSIONS
- 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.
26FUNCTIONAL 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)
27FUNCTIONAL 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.