Coastal
Emergent Wetlands:
Restoration and Protection Strategies
![]()
Emergent wetlands in coastal Texas have tremendous ecological and economic
values. Finfish,
shellfish, waterbirds and other wildlife depend on marshes to
survive. Coastal marsh vegetation also armors shorelines from erosion, filters
pollutants, enhances water quality and promotes primary production. However,
emergent wetlands in Texas have been lost due to filling, draining, dredging and
dredge disposal, bulkheading and shrimp trawling. Pumping groundwater for
industrial, commercial and residential uses has also contributed to rapid and
alarming wetland loss – especially in localized areas around Galveston Bay. As
land subsided, wetland vegetation was inundated by deep water and replaced by
less productive open water habitat.
Maintaining the economic values, fish and wildlife resources, and aesthetic qualities of the Texas Coast depends on re-establishing and restoring its wetlands. The FWS Texas Coastal Program, working in close coordination with the Galveston Bay Foundation and a consortium of federal and state agencies and conservation groups, played an integral role in providing funds and technical expertise to create an inventory identifying and describing sites included in the "Habitat Conservation Blueprint: A Plan to Restore the Habitats and Heritage of Galveston Bay." Completed in 1998, the Conservation Blueprint identifies 170 specific restoration projects and commits partners to work collaboratively to restore 24,000 acres of Galveston Bay’s coastal emergent marshes and seagrass meadows by the year 2010. Recently, the Coastal Coordination Council, the governing body of the state’s Texas Coastal Management Plan, agreed to fund a habitat restoration site inventory for the entire Texas coast. The FWS Texas Coastal Program is committed to lend its expertise and support to complete this broader coastwide project, for the first step in restoring habitat is to identify and prioritize potential restoration sites.
Where sites have been identified, restoration projects are being implemented by cooperative working groups that capitalize on the capabilities of various federal and state natural resource agencies and non-governmental conservation groups. Partners typically employ the following emergent wetland restoration techniques:
The "scrape-down" technique is used to remove excess dredge material from areas that were once wetlands. By removing dredge material to the elevation of adjacent salt marsh, and then planting the area with cordgrass, emergent marshes can be re-established. Typically, channels are excavated into the dredge material to allow nutrient flow into the upper reaches of the restoration site. This method has been employed to restore approximately 60 acres along the I-45 approach to Galveston.
The "beneficial uses" technique can be employed when dredge
material is available from nearby construction or maintenance projects. Until
recently, dredge material has typically been transported to upland disposal
sites, but many partners appreciate that dredge material can be deposited in
coastal areas where fill is needed to counteract the effects of subsidence.
Dredge material is usually broadcast as a wet slurry across a subsided area
until the elevation is
appropriate for establishing emergent marsh vegetation.
Once the dredge material settles, cordgrass is planted to encourage
re-vegetation
with native plants. Dredge material can also be used to create and maintain
islands that provide predator-free nesting for colonial waterbirds. The
beneficial uses technique can provide substantial environmental benefits and may
also reduce costs for industrial dredgers by eliminating expensive upland
disposal fees. This method has been employed to re-establish a 6 acre marsh at
Armand Bayou Nature Center in Clear Lake, a 160-acre marsh at San Jacinto
in Houston, and to create nesting habitat on several central Texas coast
islands. These projects have demonstrated that partnerships between conservation
and business interests can be forged for the benefit of all. Therefore, interest
groups have already agreed that dredge material from the upcoming Houston Ship
Canal deepening and widening project will be used to re-establish more than
4,000 acres of emergent wetlands in Galveston Bay.
The "marsh terracing" technique, pioneered in Holland and
successfully applied in coastal Louisiana, has been used at several sites in
coastal Texas, the first project was completed in 1999. In areas where
coastal subsidence has
led to wetland
loss, and erosion threatens to destroy remaining marsh, terraces
can be constructed to reduce wind fetch, help armor the shore and establish new
wetlands to provide productive fish and wildlife habitat. A marsh track hoe,
specifically designed for wetland use, pushes bottom sediments into long, narrow
terraces with shallow side slopes that rise 2 to 3 feet above the water.
Terraces are typically constructed in a series of 200 foot open square patterns.
Once constructed, terraces are planted with sprigs of cordgrass. Ultimately,
cordgrass and other emergent wetland plants will grow on the terraces, and
submerged aquatic vegetation will grow in the open water between the terraces
This restoration method has been employed to re-establish an 83 acre marsh
complex at
Pierce Marsh and a 121 acre wetland complex at Galveston Island State Park.
Geotextile tubes and rock groins placed in shallow calm seas, minimize shoreline
erosion and increase water
clarity, allowing coastal wetland vegetation to be
re-established or coastal nesting island shorelines to be stabilized.
Geotextile tubes,
best described as giant sand-filled socks, have an exterior plastic fiber
"skin" covered with a black UV-resistant shroud. Rock groins are long,
narrow mounds of rock rip-rap. Geotextile tubes and rock groins can both be effective,
but rock groins last indefinitely and create living oyster reef habitat.
Geotextile tubes, on the other hand, have an expected lifespan of 25 years and cannot
support a living marine community. However, rock groins are three times more
costly than geotubes. Geotextile tubes have been deployed offshore from Galveston Island
State Park to help restore coastal wetlands, and near Shamrock and Sundown
Islands to protect nesting islands. In other locations, such as Armand Bayou, brush
fences, snow fences and hay bales have also been used to capture silt
and minimize erosion damage on windward shorelines until marsh vegetation becomes
established.
Emergent wetland vegetation planting techniques have been refined. A
cordgrass nursery operated by Reliant Energy Inc., located in Baytown, Texas provides vegetation
for wetland restoration sites. When cordgrass is planted at the proper
elevations
and on 3 foot intervals, the restoration site will generally be fully vegetated
within two years. Cordgrass planting has been an important component of all
emergent marsh restoration projects in Galveston Bay. Oftentimes, volunteers
assist staff in completing this important, but time-consuming work.
All of these restoration techniques are relatively new and are still being refined, so collaboration, experimentation and monitoring involving many conservation-minded partners will continue, in order to determine which methods are most effective in protecting our shorelines and restoring our marshes.