Georgia Coastal Ecosystems Long Term Ecological Research Project Marsh Hammock Research 2008

Similar documents
Georgia Coastal Ecosystems Long Term Ecological Research Project Marsh Hammock Research 2009

Monitoring the marine environment

Quarterly Report. 4 December February 2014

Estuaries of South America

Aquatic insect surveys at Mount Magazine State Park and Hobbs State Park Conservation Area with implementation of an educational component

2.0 Physical Characteristics

Intense Hurricane Strike Reconstruction, Vieques, Puerto Rico

Project: Profiling Float Observations in the Aegean Sea

Title/Name of the area: Chwaka Bay, Zanzibar

Order of the Minister of Environment #39, August 22, 2011 Tbilisi

Appalachian Trail Sustainability Research Study

South Florida Coastal Water Quality Monitoring Network 4 6/06 Quarterly Report (C-15397)

KOALA BEACH ESTATE TWEED SHIRE. 20 Years On

Land-Use and Water Quality Across the Cape Fear River Basin, NC: from 2001 to Jennifer Braswell Alford, PhD

DATA-DRIVEN STAFFING RECOMMENDATIONS FOR AIR TRAFFIC CONTROL TOWERS

MANAGING FRESHWATER INFLOWS TO ESTUARIES

STUDY OF ALAQI SECONDARY CHANNEL IN LAKE NASSER

Rainfall influence upon nutrient inputs to Caribbean coastal systems. Tim Carruthers

Abstract. 1 Introduction

RE Code Names Each regional ecosystem is given a three part code number e.g For example

SeagrassNet Monitoring in Great Bay, New Hampshire, 2016

Range Expansion of Black Mangroves (Avicenna germinans) to the Mississippi Barrier Islands

Species: Wildebeest, Warthog, Elephant, Zebra, Hippo, Impala, Lion, Baboon, Warbler, Crane

Contaminant and Erosion Control Baseline Database for the Puerto Mosquito Watershed In Vieques,, Puerto Rico

Alex Dogonniuck, Michael Greener, Marissa Lathrop, Adam Loomis, Madison Morley

PCBS DELINEATION WORK PLAN

BENEFICIAL USE OF DREDGED MATERIAL DISPOSAL HISTORY HOUMA NAVIGATION CANAL, LA

Droughts: while tree islands can expand, can tropical hardwood hammocks VANISH? Tropical Hardwood Hammocks along a water availability gradient

Linking soils, hydrology, forest structure & productivity in. Michael S. Ross and Jay P. Sah. Everglades tree islands

Public Lands in Alaska. 200 million acres of federal land - Over 57 Million acres of Wilderness more than half the Wilderness in the entire nation

Spatial Distribution and Characteristics of At-Risk Species in the Southeast U.S.

Predicting Flight Delays Using Data Mining Techniques

Clam Framework Map Book NEFMC Habitat Advisory Panel Meeting, April 3, 2018

Biodiversity Studies in Gorongosa

Section 2 North Slope Ecoregions and Climate Scenarios

CARIBBEAN FOOD CROPS SOCIETY

DIDYMO SURVEY, LOWER FRYINGPAN RIVER, BASALT, COLORADO 2015

HEATHROW COMMUNITY NOISE FORUM

MOSE PROJECT: STATE-OF-THE-ART AND FUTURE DEVELOPMENT

With the first portion of this process complete, we anticipate the general timeline for the remainder of the process to be:

What Is An Ecoregion?

A geographic index to measure the carrying capacity for tourism in the populated centers of Galapagos

Port Hedland South-West Creek Dredge Plume Modelling Final Report Version 4 Prepared for Port Hedland Port Authority

Rainfall Appendix. Summary Statistics of Rainfall Data for Sites in the West-Central Florida. A Simple Conceptualized Rainfall/Discharge Relationship

C. Area of operation: Columbia River and Columbia River Estuary between mouth of estuary and Portland, Oregon.

Cruise Report R/V "HEINCKE" Cruise- No. HE-316 ( 06HK1001 ) 27 January - 05 February This report is based on preliminary data!

Virginian Atlantic (Ecoregion 8)

Appendix N MAINTENANCE DREDGING STATEMENT OF NEED & PERMIT COMPLIANCE. North Thousand Islands Management Plan Appendices

Cruise Report R/V "ALKOR" Cruise- No. HE-365 ( 06AK1101 ) 01 February - 13 February This report is based on preliminary data!

Connie Rudd Superintendent, Black Canyon of the Gunnison National Park

Authentic Assessment in Algebra NCCTM Undersea Treasure. Jeffrey Williams. Wake Forest University.

Priority Species, Communities, Ecosystems, and Threats

Region 1 Piney Woods

HYDRAULIC DESIGN OF THE TOURISTIC BERTHING IN ASWAN CITY

SUPPORT TO WATER RESOURCES MANAGEMENT IN THE DRINA RIVER BASIN DRAFT ROOF REPORT INTRODUCTION AND GENERAL APPROACH

Seychelles National Parks Authority Aspects of Research

Hudson Bay Lowlands Proposed Protected Areas

Coastal vessels The number of insurance accidents and accident rate fluctuation 8.0%

MONTAGUE HARBOUR MARINE PROVINCIAL PARK

VERP Assignment for Ft. Fisher State Recreation Area

Environmental Impact Assessment of the dredging operations and aids to navigation works in the Argentina s Santa Fe Confluencia waterway.

Agritourism in Missouri: A Profile of Farms by Visitor Numbers

WORKSHEET 1 Wilderness Qualities or Attributes Evaluating the Effects of Project Activities on Wilderness Attributes

FOR SALE Belize s World Heritage

Intermediate report. Letter of agreement FAO - GCB/RAB/013/ITA

Hydrological study for the operation of Aposelemis reservoir Extended abstract

Eastern Lake Ontario Beach User Survey 2003/2004.

Labrador - Island Transmission Link Target Rare Plant Survey Locations

Archaeologists for Hire: An In-Class Activity

Jane C. Waldbaum Archaeological Field School Field Report: Cooper s Ferry Archaeological Field School

STUDY GUIDE. The Land. Chapter 29, Section 1. Both. Terms to Know DRAWING FROM EXPERIENCE ORGANIZING YOUR THOUGHTS

DOW Number: Survey ID Date: 08/21/2018. Windom Southern

Alternative 3 Prohibit Road Construction, Reconstruction, and Timber Harvest Except for Stewardship Purposes B Within Inventoried Roadless Areas

New measurements techniques

Terrestrial Protected Area Nomination: Central Mangrove Wetland South-West, Grand Cayman

ETOBICOKE CREEK NORTH TRAIL PROJECT. May 18, 2017 at Michael Power High School 105 Eringate Drive, Etobicoke ON M9C 3Z7

A GEOGRAPHIC ANALYSIS OF OPTIMAL SIGNAGE LOCATION SELECTION IN SCENIC AREA

IMPACTS OF THE RECENT TSUNAMI ON THE BUNDALA NATIONAL PARK THE FIRST RAMSAR WETLAND IN SRI LANKA

TOWPATH MOWING GUIDELINES

Minnesota Department of Natural Resources

The search results explanations of hydrological data

Figure 1.1 St. John s Location. 2.0 Overview/Structure

CHAPTER 241. SAND BYPASSING TO "PLAYA DE CASTILLA" (HUELVA SPAIN) Jose Fernandez (1) Gregorio Gomez Pina (2) Angel Mufloz (3)

ALLOMETRY: DETERMING IF DOLPHINS ARE SMARTER THAN HUMANS?

LAKE SURVEY REPORT DRAFT VERSION PRELIMINARY DATA (AS OF 07/24/2018) Fisheries Management. DOW Number: Survey ID Date: 07/16/2018

BRAND-OGRAPHY. Katarina Baumann

Finding sources of fecal coliform bacteria in stormwater runoff

PERFORMANCE MEASURE INFORMATION SHEET #16

Map 1.1 Wenatchee Watershed Land Ownership

An Econometric Study of Flight Delay Causes at O Hare International Airport Nathan Daniel Boettcher, Dr. Don Thompson*

Monitoring the Environmental Status of the Heart of Borneo

Wilderness Research. in Alaska s National Parks. Scientists: Heading to the Alaska Wilderness? Introduction

Ecosystem context in the Environmental Impact Assessment of the Dredging Operations in the Argentina s Santa Fe

MINIMUM REQUIREMENTS DECISION GUIDE WORKSHEETS

Lake Trout Population Assessment Wellesley Lake 1997, 2002, 2007

The Past, Present, and Future of Nortek and Glider Measurements

A COMPARISON OF SURFACE IMPACT BY HIKING AND HORSEBACK RIDING ON FOUR TRAIL SURFACES IN GREAT SMOKY MOUNTAINS NATIONAL PARK

Visual and Sensory Aspect

Final. Hydroacoustic and Airborne Monitoring at the Naval Station. Mayport Interim Report June 2015

Coverage of Mangrove Ecosystem along Three Coastal Zones of Puerto Rico using IKONOS Sensor

Transcription:

Georgia Coastal Ecosystems Long Term Ecological Research Project Marsh Hammock Research 2008 Participating Investigators: M. Alber 1, C. Alexander 2, S. Pennings 3, S. Joye 1, C. Meile 1, A. Burd 1, W. Moore 4, V. Thompson 5 1 University of Georgia; 2 Skidaway Institute of Oceanography, 3 University of Houston, 4 University of South Carolina, 5 University of West Florida The Georgia Coastal Ecosystems (GCE) Long Term Ecological Research (LTER) project (http://gce-lter.marsci.uga.edu/) is investigating the underlying mechanisms by which proximity of marshes to upland habitat drives ecosystem change along lateral gradients in the intertidal zone. Our approach to this question involves taking advantage of marsh hammocks as a natural laboratory for evaluating the influence of landscape structure and freshwater input on marsh processes. The hammock research includes basic characterization of groundwater flow as well as physical and biological characteristics at selected sites, experiments designed to understand the effects of manipulating water flow on marsh processes, and modeling. Our activities this past year included processing samples from the broad survey conducted in 2007; continuing archeological studies; and instrumenting selected hammocks for intensive study. 2007 Survey The 2007 survey involved sampling 55 hammocks of varying sizes and origin. The work included intensive characterization of each site in terms of its geomorphology, stratigraphy, water table characteristics, and flora and fauna. Our analyses to-date suggests that there are differences in grain size, pore water salinity, and plant community in hammocks of different origin and/or size. Figure 1. Grain size distribution in hammocks of Holocene (black), Pleistocene (green), and dredge spoil (red) origin. Grain size analysis (C. Alexander) shows clear differences in the sediment associated with hammocks of different origin: the average grain size of hammocks created by dredge spoil is coarser than that of hammocks of Holocene origin, which is in turn coarser than those of Pleistocene origin. As expected, the percent sand in Holocene hammocks is greater than that in those of Pleistocene origin. An example comparing the grain size distributions of the sediments from three hammocks is shown in Figure 1. Hammocks created by ballast stone are comprised of large rocks and do not have soil suitable for grain size analysis.

Although there was variability in pore water salinity of the different hammocks sampled, there is an indication that salinities were lower on larger hammocks. This is consistent with our predictions, based on the fact that these hammocks have larger water tables. Nutrient data are still being evaluated but no statistical differences were observed in our initial analysis of pore water dissolved organic carbon and total dissolved nitrogen concentrations. Data on the characteristics of the plant community in the high marsh adjacent to the upland area of the hammocks were collected by A. Lynes (MS student, UH) and analyzed by C. Hladik (PhD student, UGA) (Figure 2). Borrichea frutescens was most often the dominant plant in quadrats sampled in the high marsh bordering hammocks of ballast stone, Holocene, and Pleistocene origin. Spartina cynosuroides was frequently the dominant plant on dredge spoil hammocks. Ballast stone and dredge spoil hammocks tended to have fewer species appearing as dominant, while there were more species appearing as dominant on Holocene and Pleistocene hammocks. Notably, Juncus roemerianus was never dominant on ballast and dredge hammocks. Figure 2. Dominant plants observed in quadrats sampled in the high marsh of hammocks of different origin. Plant species: Juncus romerianus (JR), Spartina alterniflora (SA), Spartina patens (SP), Salicornia virginica (SV), Distichlis spicata (DIST), Batis maritima (BM), Borrichea frutescens (BF), Spartina cynosuroides (SC). There were also differences in the plant communities of hammocks of different size classes. Species diversity was greater on smaller hammocks and decreased with increasing hammock size, for both Holocene and Pleistocene hammocks. B. frutescens had the highest frequency of dominance on smaller hammocks; J. roemerianus was most dominant on hammocks of intermediate size; and S. patens had the greatest frequency of dominance on larger hammocks. Statistical analysis (non-metric multidimensional scaling) of plant community structure to evaluate differences in both hammock size and origin is ongoing. The data collected from this effort are now being input into both GIS and Access to develop a synchronized database. The data will be used to characterize hammocks and explore

relationships among a series of independent (i.e. upland physical characteristics) and dependent (i.e. marsh biodiversity, plant and animal distributions) variables. Archeological studies We are particularly interested in the distribution of shell deposits left by the Native American occupants, because such deposits affect soil chemistry and landform exposure, and therefore may mediate high-marsh ecosystem processes by affecting the quality and quantity of water reaching the high marsh. Other legacy effects on current ecosystems might be mediated by changes in soil nutrient structure and permeability associated with fire, latrines, and seafood processing. V. Thompson and his students and colleagues have performed archeological surveys of four hammocks to date. Surveying these areas involves shovel test probes at 20 meter intervals. All sites are mapped and drawn according to standard archaeological procedures using GPS and a total station. All observable human modification to the landscape such as existing historic structures, canals, fences indicating livestock, etc. are also included. Thompson is also currently working on a database that includes reconnaissance information on over 100 islands. Thompson, J. Turck (PhD student, UGA), and C. DePratter (USC) will deliver papers based on the hammock work in symposiums at the Southeastern Archaeological Conference and the Society for American Archaeology meeting in Atlanta (April 2009). Intensive hammock research The marsh/upland surveys described above are designed to evaluate how high marsh habitats are related to a range of upland characteristics, but they will not provide detailed measurements of water flow paths or biogeochemical processes, both of which we hypothesize serve to mediate the observed distributions of plants and animals. We therefore plan intensive studies designed to characterize freshwater inflow to high marsh communities in more detail, to relate it to upland characteristics, and to determine how it affects marsh community structure. Figure 3. Locations of wells (yellow) and vibracore samples (white) on a Holocene (HNI1) and Pleistocene (PCI29) hammock. Tables show the dominant vegetation at each location. This past year we selected two hammocks for more detailed study: HN_I_1 is of Holocene origin and is located adjacent to Blackbeard Island to the north of Sapelo; PC_I_29 is of Pleistocene

origin and is located adjacent to the south end of Sapelo Island. These are of similar size, with similar vegetation zones in the high marsh. We set up transects in each hammock that run from the nearby upland (Blackbeard and Sapelo Islands, respectively), through the marsh, and up and over each hammock to the marsh adjacent to the Sound (Sapelo and Doboy, respectively) (Figure 3). C. Alexander led a field team that took vibracore samples along the transects to get detailed information about stratigraphy. These cores show that the sedimentology of these features argues for distinctly different physical and stratigraphic processes dominating their formation. The morphology of the Holocene and Pleistocene marsh islands differs significantly, with the former being long and linear, and the latter more equidimensional. Stratigraphically, Holocene marsh islands consist of fine sand beds resting unconformably on older marsh muds, which grade downward into interbedded tidal channel deposits. Pleistocene hammock stratigraphy is more varied, exhibiting fine to medium sandy beds to marsh muds, is dominated by interbedded channel deposits, and represents a longer time over which formation and modification has occurred (Figure 4). Pleistocene hammocks also frequently exhibit an overprint of Native American habitation and usage during the past 4,000 years, in the form of shell middens. Accelerator Mass Spectrometer C-14 and Optically Stimulated Luminescence dating are being used to constrain the times over which these features formed, and grain size and x-radiography illustrate the differences in sedimentary processes important in the genesis of each. The vibracore results were used to guide the placement of wells. Wells were placed in sand layers in order to prevent clogging and to allow sampling of a continuously connected groundwater source along the entire distance of both transects. The stratigraphy is very complicated at the Pleistocene site, however, and it is unlikely that every well is located in the same groundwater source. In addition to the vibracore stations, two additional lateral wells were installed at HN_I_1 approximately 5 meters to either side of the main transect near well #4 in order to get data on lateral inflow of groundwater. An additional upland well will be installed at this site in order to obtain a true zero salinity end member. The wells range in depth from 41 to 110 cm below a constant zero datum (99 to 232 cm below the surface). At PC_I_29, the two lateral wells are located near well #6. Well depths at this site range between 75 and 168 cm below a zero datum (130 to 247 cm below the surface). Pressure, salinity, and temperature loggers were placed into the select wells at both sites to collect data at 10-minute intervals; these data will be used in the groundwater modeling efforts. Groundwater biogeochemistry and radium samples were collected in August and September 2008. Sample collection will continue on monthly intervals, with additional samples planned to capture spring/neap tide and storm event signals.

HNi1 Vibracore Transect Generalized PCi29 Vibracore Transect Generalized Figure 4. Stratigraphic profiles obtained from vibracore samples taken at HNI1 and PCI29. Figures show relative surface elevation along the transect.