Tidal Wetlands Studies
Started: 3rd
Quarter 1999
Completed:
Third Qtr 2003
Brief description:
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The reliability of
vegetation maps produced through remote sensing methods is contingent
upon the results of a formal accuracy assessment. Such an accuracy
assessment is conducted by field inspection and examination of detailed
aerial photography of randomly selected locations that represent the
variability of vegetation signatures within the marsh.
USFWS identified this work as necessary for them to compare
to Dr. Kitchen's earlier work to the Tier I findings and verify the
overall study. |
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Marsh salinity field data
collection |
The goal of this work is
to provide sufficient data to allow for determination of the
relationship between interstitial salinity in the marshes and salinity
within the adjacent river channels. |
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Marsh vegetative survey |
The goals of this work
are to (1) update and expand the existing information regarding the
distribution of plant species within the tidal fresh water and brackish
marshes of the Savannah National Wildlife Refuge, and (2) continue to
define the environmental factors that determine the plant distributions. |
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Marsh vegetation survey by USFWS |
This work will establish
6 additional study sites comprised of 6 transects and an array of 24
shallow wells for monitoring of interstitial salinity. Salinity
monitoring and vegetation sampling will be conducted. Digital
videography work will be collected to provide baseline data on the
feasibility of using this technique to conduct routine monitoring of
vegetation study sites. USFWS researchers will participate in formal
accuracy assessment and sediment/marsh variability reconnaissance
efforts with ATM researchers. |
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SNWR freshwater marsh continued
vegetation monitoring |
This work will provide for continued
monitoring of all established vegetation study plots, including the 10
FWS transect areas (seven marsh sites, as per methods of Latham, 1991
and the three tidal forest sites using point-centered quarter transect
techniques.) This work will provide for
continued monitoring of the 10 quadrats established by ATM during the
1997 study, as well as collection of data on additional Rapid
Assessment Plots (RAP). Quadrat data will
be collected during both the early and late growing season. |
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SNWR freshwater marsh water
level study |
This work will provide detailed data on
hydrologic regimes within the specific vegetation associations
identified through vegetation monitoring and mapping.
Water level monitoring instrumentation will be installed at
chosen locations to determine hydrologic regimes within distinct
vegetation association. In addition, the
instrumentation will be used to determine to what extent the floating
vegetation mats rise and fall with the tide. The
instrumentation will be moved to various locations for the duration of
the project to cover the range of vegetation associations found within
the project area. For subsequent use in
the marsh succession model, the water level data will be related to
marsh surface elevations as determined by GPS survey. |
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SNWR freshwater marsh
topography survey |
A key
component of the spatial aspect of the marsh succession model will be
marsh topography. Survey grade elevations will be made at each of the
10 FWS vegetation monitoring sites along the floodplain.
These marsh elevations will be tied to the results of the
water level study to define hydrologic signatures.
The topographic survey will be conducted using GPS survey
equipment. |
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SNWR freshwater marsh sediment
characterization/mapping |
The data to date
strongly indicate that vegetation distribution is heavily influenced by
sediment characteristics. Two primary
sediment characteristics will be investigated in this work: (1) the
locations of sediments that support floating vegetation mats, and (2)
the locations of sediments that support the production of hydrogen
sulfide gas or methane gas. Some
investigators hypothesize that floating vegetation mats are able to
support relatively high plant diversities because, since they float,
they are flooded less often than plants that are rted into a firm
substrate. The marshes of highest plant
diversity within the study area exist as floating vegetation mats. This work will map the areas of floating mats
for incorporation into the marsh succession model.
Field mapping will be conducted in conjunction with
collection of Rapid Assessment Plot data and other ongoing fieldwork. Ground penetrating radar (GPR) may be used to
assist in mapping substrate types in selected locations.
GPR data will be augmented and verified by extraction of
sediment cores. In addition, production of
hydrogen sulfide or methane gas may be a very sensitive indicator of
areas that are receiving inputs of saline water during incoming tides. This work will also provide for collection of
sediment samples at various locations throughout the study area. These samples will be analyzed in the lab for
their potential for producing either hydrogen sulfide or methane gas
and assessed for their contribution to production of floating mats. |
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SNWR freshwater marsh
transplanting experiments |
This work is intended to
translocate and transplant intact cores of plant/substrate units in
such a fashion as to cross transplant within, between, and among tidal
marsh types (fresh, intermediate and brackish) while documenting
subsequent vegetation responses, if any over time.
In addition to confirming or clarifying correlational
results of the other field studies, this technique was found to be
extremely valuable to previous studies (Pearlstine et al. 1990) for
providing time-lines for vegetation responses as well as indications of
ecological community structural changes due to hydrologic alterations. |
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SNWR freshwater marsh continued
salinity monitoring |
Except for the salinity
monitoring conducted during the summer of 1999, there has been an
absence of any long-term salinity monitoring subsequent to the removal
of the time gate. However, even the summer
1999 monitoring did not capture seasonal or annual salinity dynamics in
the marshes. Data regarding these dynamics
are critical to defining the ecological functioning of the marsh. This
work will continue the marsh salinity monitoring initiated during the
summer of 1999 by permanently installing a YSI 6000 XLM salinity meter or comparable salinity meter in each of the 10 permanent study plots. |
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SNWR freshwater marsh salinity
spatial synoptic sampling |
Salinity in the marsh substrates is one of
the principal community structuring factors the tidal wetlands of the
Savannah River. Meters in ten transect
sites provide ideal information on the temporal dynamics of salinities
at specific sites. To maximize the value
of this information it is necessary to complement this long-term
spatially limited information (10 sites) with short-term, spatially
intense synoptic sampling (approximately 100 sites) to resolve spatial
distribution of salinity across and up and down the floodplain gradient. This sampling would be conducted by grabbing
samples at pre-selected grid-point locations across the wetland complex
from a roving airboat outfitted with GPS navigation. It would be
scheduled to co-incident with the 2 major wetland plant samplings that
correspond to the early and late growth season time points. |
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SNWR freshwater marsh tree gap
analysis |
The tree community structure at various sites
within the floodplain is a reflection of past and historic hydrologic
conditions. A tree “gap” study will be
conducted within the tidal forested transect sites previously
established and monitored for breeding bird surveys.
The intent is to document the relationship between tree
canopy species and the sapling/seedlings in the various regeneration
layers. This analysis will distinguish how
present hydrologic regimes may compare to the previous conditions under
which the canopy trees were established. These
sites are unlikely to occur on the transects proper and will require
finding tree fall sites in the immediate vicinity of the transects or
as proximal as feasible. |
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SNWR freshwater marsh sediment
characterization/Mapping (Spatial synoptic analysis) |
In addition to the
sediment sampling initiated previously at each of the 10 FWS permanent
study sites, a synoptic series of regularly grid-spaced sites will be
sampled in conjunction with seasonal (early and late growing season)
vegetation sampling along the upstream/downstream gradient. These data will be used to create a substrate
characterization set of GIS layers to define transition and breakpoint
regions representing the spatial boundaries of marsh zones from fresh
to sub saline conditions. This work is
essential to developing a spatial characterization of marsh substrate
types across the various gradients of hydro periods, salinities,
riverine inputs, and tidal influences (tidal subsidies).
This information is essential to the implementation of
spatially based vegetation succession modeling. |
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SNWR freshwater marsh
vegetation change analysis |
This work will continue
a study already initiated by the USFWS based on other sources of
funding. The work will be based on
analysis of aerial photography and satellite imagery to determine
changes in vegetation signatures over time. A
primary aspect of the analysis will focus on the changes in the shrub
swamp located in the transition zone between the tidal forest and the
tidal freshwater marsh. Some field
observations have indicated that the shrub cover has been increasing in
this area. Comparisons between historical
imagery and current imagery will be made to confirm and quantitate this
trend. |
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Marsh succession modeling |
The goals of this work
are to integrate data collected under the field data collection works
into wetland impact prediction model. This
model will be a geographic information system (GIS)-based spatial model
that will predict changes in wetland vegetation distribution caused by
salinity and water level changes associated with harbor deepening. A further goal of the model will be to study
potential long-term (50-year) changes in vegetation distribution
resulting from sea level rise. |
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SNWR freshwater marsh nekton
study |
In order to determine
the nektonic usage of the various marsh types, replicate flume net
traps (as per McIvor et al. 1989) will be placed in critical tidal
exchange points between the dredged channel networks and the adjacent
expansive intertidal marshes. The net
traps will be set on the marsh surface-proper, situated transverse to
specific topographic depressions where tidal flows tend to be confined
and collected between the marshes and adjacent channels.
The sides of the mouth of the traps will extend to the lower
tidal elevation limit of the emergent vegetation to the upper limit of
the high tide water surface elevation. Cod-end
pieces will be attached variously to the ends of the trap to collect
nekton entrained through the flume on the rise and fall of the tides. Flume traps will be established at selected
points, as described above, in each of the three marsh types along the
salinity gradient. These sites should
occur in the proximity of established vegetative sampling transects.
Data obtained from the traps will be coordinated with other
investigators sampling fish communities in the river and sub tidal
reaches of the canal network to determine what portion of the fish
species pool occupy and use the marsh surface. |
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SNWR freshwater marsh migratory
bird study |
Avian use of the four major tidal wetland
types within the Savannah National Wildlife Refuge will be assessed
seasonally. These types include tidal swamp forests, fresh-,
intermediate-, and brackish- marshes. Study design, to be completed in
March 2000, is intended to document avian use by fall and spring
migrants, and selected over-wintering birds. The design will focus on
both spatial and temporal use, incorporating replicate surveys to
ensure statistical validity. Sampling will
begin in the fall of 2000 and run through the spring of 2001. Sampling
methods will include point counts, mist netting and response to call
recordings. Only birds using the habitats examined will be recorded,
flyovers will not be included in the survey results. Sampling times
will be centered on peak migration times, the last week of September
for fall migration and the first week of May for spring migration.
Winter sampling will be from December through March. |
Current status:
Complete
Links:
Tidal
Wetlands Study Scope of Work
Tidal
Resource Utilization Studies Report