28 research outputs found

    Community-Based Watershed Planning in the Kingston Lake Watershed of Northeastern South Carolina

    Get PDF
    2008 S.C. Water Resources Conference - Addressing Water Challenges Facing the State and Regio

    Community-Based Watershed Planning in the Kingston Lake Watershed of Northeastern South Carolina: Activities During 2008-2010

    Get PDF
    2010 S.C. Water Resources Conference - Science and Policy Challenges for a Sustainable Futur

    Stable isotope geochemistry of nitrogen in marine particulates

    Get PDF
    Submitted in partial fulfillment of the requirements for the degree of Doctor of Philosophy at the Massachusetts Institute of Technology and the Woods Hole Oceanographic Institution January 1983Isotope studies of nitrogen and carbon were undertaken to investigate the fate of particulate organic matter (POM) during its residence in the water column and after deposition on the seafloor. The processes focused on were water-column transformations and sedimentary diagenesis. Sampling sites were chosen to provide POM subject to different specific mineralization processes (nitrification, denitrification, and sulfate reduction), different lengths of water column (duration of the mineralization process), and differences in the size of the organic-matter flux. The δl5N and δ13C of plankton, POM, and sediments from several oceanic sites were related to biological and hydrographic processes identified from nutrient, temperature, and salinity profiles. This was done to determine what effect these processes have on the δ15N of POM. Four stations were studied in the upwelling area off the coast of Peru and one station was studied in the Gulf of Maine. Important factors controlling the δ15N of plankton appear to be the concentration and δl5N of nitrate in the surface waters, and the relative zooplankton and phytoplankton abundances. Plankton from the Peru Upwelling Area are enriched in 15N as compared to plankton from other parts of the world's oceans where denitrification is absent. This enrichment may be due to the assimilation of 15N-enriched nitrate, produced by the selective reduction of 14N during denitrification. Zooplankton are 3 to 4% enriched in 15N as compared with phytoplankton. Production of 14N -enriched fecal pellets is suggested as a mechanism for this trophic enrichment. In the surface waters, the δl5N of POM is similar to that of plankton. In the Peru Upwelling Area, the δ15N of POM from the oxygen-deficient waters decreases with increasing depth. In the Gulf of Maine, below the euphotic zone in the oxic deep waters, the δ15N of POM increases with increasing depth. The difference in isotopic alteration may be due to the effect of different redox conditions on the mechanism and sequence by which specific organic nitrogen compounds, variably enriched in 15M, undergo degradation. Furthermore, bacterial growth on nitrogen-poor particles in the deep waters of the Peru Upwelling Area may contribute to the low δ15N of POM. In contrast to the large range in δ15N (-2 to +17%) of the POM, the range of δ15N in the sediments is small (+5 to +9%). Within a core, the average variation in δ15N was only 1.8%. Temporal variability in the δ15N of sedimenting POM and benthic activity appear to be important in determining the δ15N of the sediments. The large changes in POM concentration and isotope content at the sediment/water interface as compared with the more constant values found down-core, suggest that processes occuring at the sediment/water interface are critical, although bioturbation may also be important in determining the δ15N of oxic sediments. If diagenesis causes a significant loss of organic matter, profiles of organic carbon and nitrogen contents should show decreases with increasing depth and C/N ratios should increase with increasing depth (Reimers, 1981). Since none of the sedimentary profiles exhibited such trends, it is concluded that diagenesis was insufficient to erase the percent carbon, nitrogen and C/N ratio signatures generated by the POM flux and alterations at the sediment/water interface. Temporal variability in the δ15N of bottom-water POM may be caused by changes in deep-water currents which transport POM horizontally and to changes in bacterial and possibly other biological activity in the water column. This thesis work suggests that δ15N may be a useful tool in studying the geochemistry of POM in the marine environment. In addition, this research has shown that interpretation of the sedimentary 15N record must include consideration of isotopic alteration associated with bacterial remineralization of POM and benthic activity.Funds for this research were provided by the Massachusetts Institute of Technology / Woods Hole Oceanographic Institution Joint Program in Oceanography, the National Science Foundation under Grant No. OCE-8024442, and the Andrew W. Mellon Foundation through the Center for Coastal Research of the Woods Hole Oceanographic Institution

    Application of qPCR Technologies in Stormwater Source Tracking and Determination of Host Contributions of Fecal Indicator Bacteria

    Get PDF
    2012 S.C. Water Resources Conference - Exploring Opportunities for Collaborative Water Research, Policy and Managemen

    Assessment of Water Quality Benefits from Stormwater Treatment Train and Ocean Outfall for the Main Street Drainage Basin in N. Myrtle Beach

    Get PDF
    2014 S.C. Water Resources Conference - Informing Strategic Water Planning to Address Natural Resource, Community and Economic Challenge

    Long Bay Hypoxia Monitoring Consortium

    Get PDF
    In October 2011, the coastal municipalities of North Myrtle Beach, Myrtle Beach, Surfside, and Horry County signed a resolution, under the aegis of their Coastal Alliance of mayors, to develop and implement the Long Bay Hypoxia Monitoring Consortium. The goal of this consortium is to support monitoring and studies that further characterize hypoxia and its causes in Long Bay. The baseline data will enable assessments of water quality management efforts. Monitoring stations are to be maintained at three piers, Cherry Grove (NMB), Apache (Horry County), and Second Ave N. Pier (Myrtle Beach). Turbidity and chlorophyll sensors will be deployed at two piers and radon detectors at three piers. All piers will have weather stations. Data will be accessible via a real-time public website. Biological responses to low dissolved oxygen (DO) will be assessed via monitoring of larval recruitment and net plankton. The S.C. Department of Natural Resources (SCDNR) is also conducting creel surveys at the piers. These efforts are being coordinated with a marine education outreach campaign that includes signage at the piers, presentations at pier events, and web-based content

    Watershed-Based Planning for Murrells Inlet: Source Assessment of Fecal Bacteria using Volunteer and Shellfish Sanitation Program Data

    Get PDF
    2014 S.C. Water Resources Conference - Informing Strategic Water Planning to Address Natural Resource, Community and Economic Challenge

    Crabtree Swamp Stream Restoration in Horry County, South Carolina

    Get PDF
    2010 S.C. Water Resources Conference - Science and Policy Challenges for a Sustainable Futur

    Watershed Management Planning for the Murrells Inlet Estuary using GIS: Delineation, Assessment, Identification, and Solutions for Fecal Coliform Loading,

    Get PDF
    2014 S.C. Water Resources Conference - Informing Strategic Water Planning to Address Natural Resource, Community and Economic Challenge
    corecore