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St. Petersburg Coastal and Marine Science Center > Geologic and Morphologic Evolution of Coastal Margins > Research > Subsidence and Coastal Geomorphic Change in South-Central Louisiana

Geologic and Morphologic Evolution of Coastal Margins

Subsidence and Coastal Geomorphic Change in South-Central Louisiana

Location map showing land loss from 1932 to 2004 for Louisiana coast and study area.
Above: Location map showing land loss (red) from 1932 to 2004 for Louisiana coast (A) and study area (B). Land loss in southern coastal Louisiana is caused by conversion of marsh to open water. Land loss data used in figure is from Morton and others (2010) and Barras and others (2008). [larger version]

Relative ranges and rates of subsidence by physical properties
Above: Relative ranges and rates of subsidence by physical properties (figure modified from oral and written communication, James Syvitski, 2013). Processes deeper in the Earth's crust (i.e., faulting and flexure of the lithosphere) contribute relatively little to land-surface subsidence rates (typically <1 millimeter per year (mm/yr)), deltaic sediment loading leads to lithospheric subsidence rates in key portions of the Mississippi Delta of ~0.15 ±0.07 mm/yr relative to the Chenier Plain, the common, long-term process that drives lithospheric subsidence throughout the Gulf of Mexico is glacial isostatic adjustment (at least 0.4 mm/yr along the central U.S. Gulf Coast), and compaction, fluid extraction, and growth faulting are potentially large factors with need of a major research effort, given their spatiotemporal variability. [larger version]

Schematic of proposed barrier island subsidence sampling and monitoring set up.
Above: Schematic of proposed barrier island subsidence sampling and monitoring set up. Primary procedure: 1) install 1st order benchmarks to monitor surface elevation (subsidence) across barrier island; 2) collect topography and bathymetry data (including inlets at each end) to compare with archived data and elevations; 3) collect auger cores (~10 to 20 meter deep) for stratigraphy; 4) install extensometers to monitor compaction following core collection; and 5) collect short cores as proof-of-concept identifying subsidence versus erosion by comparing short-and long-lived isotopes (7Be/234Th, 210Pb/137Cs, and Rad7). [larger version]

High historical land-loss rates in coastal Louisiana have resulted in the conversion of approximately 5000 square kilometers (km2) of formerly emergent wetlands to open water since the 1930s. Evaluating subsidence is complicated because rates are highly variable both spatially and temporally.

Geologic Processes Driving Coastal Subsidence

Barrier Island and Barrier Shoreline Subsidence - Stratigraphic Compaction Relative to Restoration

Relative sea-level rise and subsidence are leading to the inundation of shorelines, barrier islands, and wetlands of Louisiana, Mississippi, Texas, and Alabama. Reed (2009) reported that observed rates of subsidence span two orders of magnitude in coastal Louisiana with the largest values exceeding 10.0 millimeters (0.4 inches) per year [0.91 meters (3 feet) per century]. A relative decrease in elevation (subsidence) with respect to sea level results in land and habitat loss, and endangers infrastructure and ecosystem health in and around Louisiana’s coastal communities by increasing the likelihood of flooding and damage from storms.

The focus of this study is subsidence induced by shallow compaction over the past 10,000 years and relative sea-level rise rates impacting coastal shorelines, barrier and marsh islands, and nearshore coastal systems. As a part of this study, several types of data are needed to analyze the effects of subsidence on coastal change. Data types that will be analyzed include lidar, bathymetry, sediment texture and stratigraphy, and inlet hydrodynamics. These data will be used to refine and assess geomorphic models.

The strategy is to select a barrier island site that will be restored in the near future (for example, Isle Dernieres or Timbalier). Prior to restoration, it is necessary to characterize the physical environment including topography, bathymetry, and sedimentology of the barrier island system. First order benchmarks and extensometers will be installed to establish a baseline condition and measure future elevation change. The data collected from these tasks will be used to model potential geomorphologic change (for example, shoreline change resulting from island breaching or sediment erosion and redistribution resulting from washover processes).

Main objectives

Partners and associated projects: CMG –NGOM2 and Subsidence, CRMS, UNO, potentially LSU, Inlet Change Analysis, and Geomorphic Modeling.

References

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