Upload
barrie-howard
View
215
Download
0
Tags:
Embed Size (px)
Citation preview
Shoreline Stabilization and Changes in Sediment Composition Associated with Small-Scale Oyster
Reefs in South Carolina
Michael HodgesNancy Hadley
Loren Coen
Steve Roth
Lindsay Goodwin
Majbritt Bolton-Warberg
The South Carolina Oyster Restoration and Enhancement Program (SCORE)
was established to:• Involve citizens in oyster
restoration activities• Educate the public and
foster environmental stewardship
• Utilize volunteer assistance to recycle shell
• Use volunteer manpower to establish multiple research platforms annually along South Carolinas coast and aid in data collection
In Five Years, SCORE Has
• Established 128 reefs (2,115m2) at 29 sites along 320 km of coastline
• Encompassed a broad spectrum of environmental conditions
• Involved over 2,000 volunteers/over 15,000 hours of service
• Trained weekly water quality monitors at most of these sites
We Monitor Regularly for the Following
1. Marsh erosion
2. Marsh expansion
3. Sedimentation rate and composition
4. Chlorophyll a
5. Water quality (pH, DO, Salinity, Water Clarity, Temp)
6. Utilization by other organisms
7. Population parameters
8. Reef observations
Marsh Erosion• Natural phenomenon caused by
winds, waves, currents, and tides
• Destabilization of fringing marsh is a cause for concern and seriously affected by erosion
• Human activities such as boat traffic, wetland drainage, and dredging increase rates of erosion
• Oysters act as natural breakwaters for fringing marsh to help decrease the rate of shoreline loss
SCORE Erosion Site Results, 2001-7/06SCORE Erosion Site Results, 2001-7/06
Mean Overall ErosionMean Overall ErosionMonthly Mean Erosion RatesMonthly Mean Erosion Rates
Mean monthly rates ranged from 1.3 – 5.5 cm Overall shoreline losses ranged from 40.5 – 331.3 cm.
Numbers in columns indicate total length of assessment, 21 – 59 mo.
Spartina Expansion• Although marsh edge continues
to retreat, overtime Spartina is growing seaward
• Expansion has been noted at 10 sites, significant expansion at 9 sites
• Generally takes place 2.5-3 years post-construction
• Appears to be associated with the accumulation of soft sediments and stabilization behind reefs
• Has grown seaward as much as 13 meters at some sites
Marsh Expansion These are totals for the original reefs deployed at these sites, negative numbers represent retreat of marsh
Site Mean Expansion
(m)
Max Expansion
at Single Reef
(m)
Length of Deployment
(months)
Kiawah -1.0 0 29
Boy Scout -0.6 3.5 65
Waddell 3.3 6.3 52
Dataw 3.5 6.2 65
Palmetto 4.6 8.5 65
Trask 7.6 13.9 52
Shoreline Changes at Palmetto I slands County Park 2001-2005
-10
-8
-6
-4
-2
0
2
4
1 3 5 7 9 11 13 15 17 19 21 23 25 27 29
Location of Forward Marsh Edge Relative to Reef (m)
Oyster Reef 2005 2001-02 2003
Oyster reef
Creek
High Ground
Marsh
(m)
Sediment Depth Poles
• Used to measure rate at which sediments settle at reefs
• Poles are 40 cm in length
• Placed behind reefs• Measured quarterly or
bi-annually
Sediment Grain Size Analysis
• We wanted to examine pre-construction sediment composition vs. post-construction sediment composition
• There is a significant difference in the sediment composition accumulating behind reefs vs. sediment composition not associated with constructed reefs
(p= .003)
• At all sites monitored , there has been an increase in the amount of fine sediments settling at our reefs.
• The sediment is either washing down from above salt marshes or settling out with reduced flow rates around new reefs
0
10
20
30
40
50
60
70
80
90
100
pre-
construction
2004 2006
pre-
construction
2004 2006
pre-
construction
2004 2006
Trask Landing Waddell Center Palmetto Park
Changes in Sedimentation Following Reef Construction, Year Two, and Year Four
Mud
Sand%
Co m
posi
tion
Site/Years
Conclusions• Spacing of reefs is important when considering shoreline
protection• Reef deployment aids in marsh expansion• Sediment compositions are changing at sites as reefs are
introduced• Early adaptive management techniques will help to deal
with excessive sedimentation• Using volunteers will help facilitate work load and
increase community awareness on environmental concerns
• Filling knowledge gaps of sheltered coastal systems
Future Objectives
• Continue to intensely monitor erosion behind reefs and areas not associated with reefs to see if they differ significantly
• Continue to monitor changes in sediment composition and marsh expansion
• Use findings to establish oyster restoration metrics
• Construct more reefs in Northern part of SC