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Long-Term
Monitoring Site at North Inlet Winyah Bay National Estuarine Research
Reserve, South Carolina
Dr. Erik Smith and Tracy Buck from the University of South Carolina,
Belle W. Baruch Institute for Marine and Coastal Sciences
BACKGROUND
The North Inlet-Winyah Bay National Estuarine Research Reserve (NEER)
is one of 26 sites around the coastal US. Each reserve receives funding
from the National Oceanic and Atmospheric Administration (NOAA)
and matched resources from the host state agency. The North Inlet-Winyah
Bay Reserve is hosted by the University of South Carolina,
Belle W. Baruch Institute for Marine and Coastal Sciences.
The Reserve encompasses 12,327 acres of tidal marshes and wetlands.
North Inlet-Winyah Bay NERR features high quality, ocean-dominated
waters and salt marshes in North Inlet, contrasting with the brackish
waters and marshes of Winyah Bay. The bay's estuary is dominated by
riverine discharges from a watershed impacted by agricultural, municipal
and industrial development. Former rice fields and canals provide
another system for study within the Reserve (http://www.northinlet.sc.edu/).

Figure 1. Oyster Landing (OL) monitoring site in South Carolina
STUDY SITE
The Oyster Landing (OL) meteorological and water quality monitoring
site, located at the end of the pier, is considered a fairly pristine
and undisturbed area. The pier stretches into the upper reaches of
Crabhaul Creek in the mid-western portion of North Inlet. The sampling
site is located approximately 2.8km from the headwaters of Crabhaul
Creek. The creek directly drains pine forested uplands and wetlands.
Salinity can range from 0-32 ppt. and average tidal range is approximately
1.4m.
The creek has an average depth of ~2m MHW and an average width of
~150m at MHW. The bottom is comprised mostly of oyster shell hash
with some fine sediment and detritus.

Figure 2. North Inlet Winyah Bay National Estuarine Research Reserve,
South Carolina (latitude 33o20'58" longitude 79o11'34") http://www.northinlet.sc.edu/research/Default.htm#four%20sites
PROTOCOL
The PhytoFlash was deployed at a depth of 0.5 m and was logging at
15-minute intervals. An ISCO sampler was programmed to collect samples
at two-hour intervals. Samples were processed for extracted chlorophyll
a, inorganic nutrients, and absorbance of filtered water samples.

Figure 3. Turner Design’s PhytoFlash deployed in the Self-Contained
Mode

Graph 1. Data reflecting absorbance, determined on a spectrofluorometer
at 355nm, and water level over two tidal cycles (January 25, 2006).
Absorbance is negatively correlated to water level, suggesting a strong
export of colored fractionated water on the ebb tide.

Graph 2. Absorbance, water level, and PhytoFlash blank data were used
a posteriori to “blank correct” for the PhytoFlash yields.

Graph 3. Blanks measured on the PhytoFlash and spectrofluorometer
by using GF/F filtered sample water at 19 degrees C. It is possible
to derive corrected blank values from the PhytoFlash using additional
absorbance measurements.
Dr. Erik Smith
The Belle W. Baruch Institute for Marine & Coastal Sciences
607 EWS Building
Columbia, SC 29208 |