Cape Romain National Wildlife Refuge Climate Change Impacts

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Climate Change Impacts

How will the Refuge be Affected by Climate Change? Salt marsh fragmentation by rapidly eroding tidal creeks Salt marsh submergence during high tide events leading to habitat conversion from marsh to tidal flat to open water Barrier island shoreline erosion due to wind, waves, ocean currents, sea level rise, and sediment starvation Refuge infrastructure losses due to sea level rise and erosion Loggerhead sea turtle nesting beaches, sea bird and shorebird nesting islands undergoing rapid conversion Shift in species Composition = Fewer waterfowl (ducks) more wading birds (roseate spoonbill, woodstork)

Sea Level Rise Charleston Harbor Since 1923 In the past 100 years sea levels have risen 3.15 mm/year = 1 foot 4 inches In the past 20 years 4.6mm/year = 3.6 inches in 20 years, 1 ½ feet in 100 years)

Nothing Level about Sea Level! New Moon +6-1 Half Moon +5 +4 +0.6

Flood Patterns

Can the Salt Marsh Keep Up? Key factors of the future tidal marsh acres The Capacity of the Marsh to raise and keep up with rate of Sea Level Rise. Rate of Erosion of the Seaward boundary of the marsh The availability of space for the marsh to migrate inland. Amount of head ward erosion in marsh creeks. Currently 6.2 feet/year Hughes et al (2009), Rapid headward erosion of marsh creeks in response to relative sea level rise, Geophys. Res. Lett., 36, L03602, doi:10.1029/2008gl036000.

RAPID DEVELOPMENT SINCE 1940 s 1 2 3 1968 2006 RATE OF INCISION =1.9 ± 0.8m/yr

Santee River Delta, South Carolina Area = ~36,000 km 2 ~700 km long 1940, ~3% 1986, ~80%

Summary Straight, evenly spaced channels forming rapidly Area of high regional SLR and very local SLR due to damming (increased hydro period). Accumulation limited by dams Channel network expansion relates to increased tidal prism Ability to erode the marsh facilitated by vegetation removal and bioturbation (crabs). In areas where sediment has sufficiently low strength and high RSLR may respond the same way?

NWR 29,820 Acres (45%) Salt Marsh Open Ocean 10% Undeveloped Land 3% Estuarine Water 35% Salt Marsh 45% Estuarine Beach 2% Undeveloped Land Swamp Inland Fresh Marsh Transitional Salt Marsh Salt Marsh Estuarine Beach Tidal Flat Inland Open Water Estuarine Water Open Ocean Brackish Marsh

2050 NWR 20,542 Acres (31%) Salt Marsh Open Ocean 13% Undeveloped Land 3% Salt Marsh 31% Estuarine Water 44% Undeveloped Land Inland Fresh Marsh Salt Marsh Tidal Flat Estuarine Water Brackish Marsh Swamp Estuarine Beach 1% Tidal Flat 3% Transitional Salt Marsh Estuarine Beach Inland Open Water Open Ocean

2075 NWR 11,928 Acres (18%) Salt Marsh Open Ocean 15% Undeveloped Land 2% Salt Marsh 18% Estuarine Beach 1% Tidal Flat 8% Estuarine Water 52% Undeveloped Land Inland Fresh Marsh Salt Marsh Tidal Flat Estuarine Water Brackish Marsh Swamp Transitional Salt Marsh Estuarine Beach Inland Open Water Open Ocean

5,301 Salt Marsh Acres by 2100. A loss of 24,519 Acres Open Ocean 17% Undeveloped Land 2% Salt Marsh Estuarine Beach 8% 1% Tidal Flat 11% Estuarine Water 58% Undeveloped Land Swamp Inland Fresh Marsh Transitional Salt Marsh Salt Marsh Estuarine Beach Tidal Flat Inland Open Water Estuarine Water Open Ocean Brackish Marsh * Based on 2.26 Feet SLR over next 100 years

Model of Barrier and Tidal Evolution in a Regime of Accelerated Sea-Level Rise Tidal Prism Initial Stage Tidal Prism Stage 1 Initial Stage Ebb-Tidal-Delta Volume Ebb-Tidal-Delta Volume Tidal Prism Stage 2 Stage Initial Stage 1 Ebb-Tidal-Delta Volume Tidal Prism Stage 3 Stage 2 Stage Initial Stage 1 Ebb-Tidal-Delta Volume

Severe Coastal Erosion on Raccoon Key s Sandy Point Reference 1983 Topographic Map

All That Remains of Sandy Point February, 2009 WRONG! It was gone by Halloween Prediction Gone by Christmas, 2009

Impacts on Seabird Nesting Habitat on Sandy Point Least Tern Nesting 1990 144 2008 26 92% Decline 2009 0 100% Decline Black Skimmers 1993 228 2008 0 100% Decline

Bulls Island Historic Shorelines Compared to today s shoreline: 1852: 2,950 ft 1920: 1,885 ft 1962: 870 ft 1852 2000: 225 ft 2000 1962 1920 Average rate of erosion: 20 to 25 ft/yr

Jack s Creek Jacks Creek Levee 1949-2006 Position of Levee in 1949 Current Levee constructed 1988 Redirected levee 2006

Future Breach How long before the next breach in the Levee? + 5 years

Cape Island Historic Shoreline

Cape Island 180 feet lost 1999 2006 Between 1999 and 2006, approximately 180 linear feet of beach shoreline width was lost to erosion.

Erosion on Cape Island High Tide Low Tide Photo by Steve Hillebrand

Cape Island Topography

Cape Island Highest density nesting beach of Northern Nesting Assemblage in SE U.S. 1 Represented 23% of NNA nesting Nest Protection Project Nest caging Hatcheries Relocated Nest on Cape Island Hatchery on Cape Island Global Distribution of Nesting Assemblages 1 Procyon lotor Looking for nests on Cape Island Cape Island Photo: Steve Johnson

Recovery Program Challenges Due to Sea Level Rise Suitable nesting beaches are eroding Islands likely to destabilize, fragment More nests are subject to inundation then mortality Rising global temps may affect gender ratio Increased workload needed to address above - not possible with current staff

Climate Adaptation To Relocate or Not To Relocate SLR, Severe erosion, and large tidal amplitudes - limits productivity Concerns raised about relocation Might skew sex ratios Could reduce hatchling size and emergence success possibly selects offspring from individuals that consistently select poor nest sites Unnecessary relocation or poor technique can be a threat Caretta caretta eggs being relocated

Washover Nests

Temperature determines Sex Ratio Mean Mid Third Temp ( C) 31.5 31 30.5 30 29.5 29 28.5 100% Female Pivotal 28 In-Situ 07 Hatchery 07 Hatchery 07 #1 #2 In-Situ 08 Hatchery 08 #1 Nest Type by Year Hatchery 08 Hatchery 08 #2 #3 n=231 Increase in temperature could skew sex ratios.

s Lighthouses Circa 1827, 1858 On National Register of Historic Places Remote island Less that 1 meter above sea level. Significant work needed Complicating Wilderness Area prohibitions Photo by Steve Hillebrand

What do we do now? Study Rapid Head-ward Erosion of Marsh Creeks and how Santee River sediments play a role in the growth of Marsh. Better elevation data (LIDAR) to determine where marsh will grow SET Stations in Marsh to determine level of subsidence/growth Inventory and Monitor Marsh Birds and Diamondback Terrapins for base line information on species that depend on the marsh. Jacks Creek Cross Dike?

Questions? Sunset Photo by Steve Hillebrand