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Oyster ( Crassotrea virginica ) monitoring in the St. Lucie Estuary. Melanie Parker and Steve Geiger Associate Research Scientist Fish and Wildlife Research Institute 100 Eighth Avenue SE St. Petersburg, FL 33701 Melanie.Parker@myFWC.com. Outline. Background information

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oyster crassotrea virginica monitoring in the st lucie estuary

Oyster (Crassotrea virginica) monitoring in the St. Lucie Estuary

Melanie Parker and Steve Geiger

Associate Research Scientist

Fish and Wildlife Research Institute

100 Eighth Avenue SE

St. Petersburg, FL 33701

Melanie.Parker@myFWC.com

outline
Outline
  • Background information
    • Water Flow in SE Florida
    • CERP
  • Oyster Monitoring
    • Methods
    • Preliminary results and trends
  • Summary
water flow in south florida
Water Flow in South Florida
  • Historically, drainage patterns were characterized by slow, surface flows through rivers, creeks, sloughs and marshes
    • Natural system absorbed floodwater, promoted ground water recharge, assimilated nutrients and removed suspended materials
  • As south Florida developed, the resulting canal network drastically altered the quality, quantity, timing and distribution of freshwater entering the estuaries

SFWMD

water flow in south florida1
Water Flow in South Florida

Historic Flow

Current Flow

Restored Flow

U.S. Army Corps of Engineers, Jacksonville District

comprehensive everglades restoration plan cerp
Comprehensive Everglades Restoration Plan (CERP)
  • Implemented as means of reinitiating natural freshwater flow to both coasts of south FL
  • Realized through habitat enhancement and water storage/treatment projects
  • Monitoring component of CERP addresses impacts of changed freshwater flow on flora / fauna
  • Eastern oyster chosen as a target species for CERP
water flow impacts
Water Flow Impacts
  • Current water management practices involve releases of large volumes of freshwater over short periods of time
    • Flood releases and urban runoff contain many contaminants from urban and agricultural development
    • Sudden drops in salinity lead to decreased growth, reproduction, recruitment and even death of oysters in the estuary
    • Drastic changes in salinity can increase oyster disease prevalence and intensity
  • Freshwater inflows are often too great in the wet season and too little in the dry season
cerp objectives
CERP Objectives
  • Reduce the impacts of freshwater releases
  • Restore more natural freshwater inflows into estuaries
    • More optimal salinities
    • Reduction in nutrient loads
    • Improved water clarity
  • RESULT - promote reestablishment of healthy oyster reefs
    • Added benefit to other organisms that use oyster reef habitat
oysters as an indicator species
Oysters as an Indicator Species
  • Dominant species in Florida estuaries
  • Salinity and other water quality conditions that are suitable for oysters are also ideal for many other organisms
  • Keystone species – habitat, filtration, shoreline and sediment stabilization
  • Sedentary nature of oysters allows for generation of cause-and-effect relationships between environmental conditions and oyster health
st lucie estuary study sites
St. Lucie Estuary Study Sites
  • North Fork
  • South Fork
  • Middle Estuary
  • 3 monitoring stations in each site
oyster monitoring components
Oyster Monitoring Components
  • Abundance and Distribution
  • Juvenile Recruitment
  • Reproductive

Development

  • Perkinsus marinus
    • Disease Prevalence
    • Disease Intensity
  • Water Quality
results
Results
  • CERP is a long term project
    • Potential 50 years of oyster monitoring
    • We are in Year 6 – began in 2005
  • Results are preliminary
    • No major changes in water management practices
    • General trends / Storm events
slide13

Salinity

7-9 mos

below 5ppt

2-3 mos

below 5ppt

2-5 mos

below 5ppt

slide14

Rainfall

  • 2005 – Wettest Year of study
    • Most active storm season to date
    • Hurricane Wilma in October
  • 2006 – Driest Year of study
  • 2007 – Tropical Storm Barry in June
  • 2008 – Tropical Storm Fay in August
canal control structures
Canal Control Structures

Rainfall

  • Canal 23 – S97

Water Releases

    • Canal 24 – S49
    • Canal 23 – S48
    • Canal 44 – S80
slide17

Density

Highest Live Densities: 2007, Spring 2008, and 2010

99%

Dead

slide18

Shell Height

Largest Shell Heights: Spring 2005 and Spring 2008

summary
Summary
  • St. Lucie estuary strongly impacted by water management practices
    • 2005 and 2008 die off
  • Timing and extent of freshwater releases impacts recovery time of oysters in St. Lucie
    • 2005 – 6 months of high FW flow, recovery in Fall 2006
    • 2008 – 2 months of high FW flow, spat set in November
  • Die-offs can also destroy recruitment substrate as shells become unconsolidated and buried by sediment
  • 2010 – No oyster die-off but low recruitment rates
    • Poor egg quality?
    • Poor larval survival and settlement?
next steps
Next Steps…
  • What can we do to better summarize the biological data for water management?
    • Can we determine the relationship between flow releases and salinity patterns in the estuary?
      • How do releases from the three canals impact each site?
    • Can we determine ideal water release levels (cfs) to maintain suitable conditions in the estuary?
      • Maximum rate / duration?
      • Promote adult and larval survival
    • Data Exploration
      • Can we quantify differences between sites/years with salinity?
      • Biological Parameter vs. Salinity regressions
acknowledgements
Acknowledgements

FWC Molluscan Fisheries crew

Sarah Stephenson, Janessa Cobb, Anthony Vasilas, Michael Drexler, Lindsey O’Hearn, Bethany Pierce

Former Molluscan Fisheries crew members

Bill Arnold, Brett Pittinger, Carla Beals, Brandy Brown, Jennifer Davenport, Sara Bergeron

Histology Lab Center for Biostatistics and Modeling

Yvonne Waters, Noretta Perry Erin Leone

South Florida Water Management District

Patti Gorman, Patty Goodman, Darlene Marley

FGCU– Aswani Volety

HBOI – John Scarpa