Bay Scallop Habitat Requirements Jay Leverone, Ph.D. Sarasota Bay - - PowerPoint PPT Presentation

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Bay Scallop Habitat Requirements Jay Leverone, Ph.D. Sarasota Bay - - PowerPoint PPT Presentation

Bay Scallop Habitat Requirements Jay Leverone, Ph.D. Sarasota Bay Estuary Program Presentation to the CHNEP Shellfish Restoration Needs Workshop February 23, 2011 Bay Scallop Habitat Requirements Bay scallops need seagrass to recruit,


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Bay Scallop Habitat Requirements

Jay Leverone, Ph.D. Sarasota Bay Estuary Program Presentation to the CHNEP Shellfish Restoration Needs Workshop February 23, 2011

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Bay Scallop Habitat Requirements

  • Bay scallops need seagrass to recruit,

survive, grow and spawn!

  • Questions?
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Bay Scallop Environmental Requirements

(Leverone, 1993, MML Tech Rpt 253; Two articles in Fla. Sci. 58)

  • Water Quality

– Temperature, Salinity, DO,

  • Food

– Phytoplankton composition, chl, TSS

  • Reproduction
  • Habitat
  • Hydrodynamics
  • Harmful Algal Blooms (i.e., red tides)
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SLIDE 4

Sources of Information

  • Results from a 1992-3

field and laboratory study Tampa Bay.

  • Requirements based
  • n correlations of

growth, mortality and reproduction with species-relevant measures of water quality

  • Literature

information most appropriate for Florida populations

  • f bay scallop
  • Technical Report

“Literature Search and Data Synthesis

  • n the Bay Scallop

with Emphasis on Florida Populations”

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SLIDE 5

References on relevant WQ and environmental conditions for the southern bay scallop

PARAMETER REFERENCE Temperature Tettlebach & Rhodes, 81 Dissolved Oxygen Van Dam, 54; Shumway & Sandifer, 91 Salinity Tettlebach & Rhodes, 81 Food Supply Fegley et al., 92; Calahan et al., 89 Macrophyte Abundance Ambrose, 89; Prescott, 90; Eckman, 87 Current Speed Eckman et al., 87 Turbidity Stone & Palmer, 75 Suspended Solids Dyer, 75 Predators Peterson et al., 89

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Unique Life History Differences for Florida Populations

  • Shorter life expectancy
  • Higher metabolic rates
  • Reproductive cycle occurs later in the

year

– Lower fecundity – Smaller egg size – Higher energetic cost of reproduction

  • Limits southern distribution and may

accelerate senescence

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Tampa Bay: Field Study

  • Deploy and maintain scallops at two sites

– Beacon Key – Boca Ciega Bay

  • Two deployments

– June (laboratory spawned) – August (wild scallops from Steinhatchee)

  • Collect relevant WQ data (biweekly)

– Temperature, salinity, DO, turbidity, TSS, chl a, phytoplankton composition

  • Measure biological responses (biweekly)

– Growth, mortality, reproductive development, fouling potential

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Tampa Bay Stations

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Scallop Growth

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Temperature Ranges

  • Alligator Harbor populations: 9 – 32oC

(Sastry, 1965)

  • Anclote Harbor populations: 21 – 32oC

(Barber and Blake, 1985).

  • Tampa Bay populations: 23 – 31oC
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DO Record at Boca Ciega Bay (8/27 – 10/27/1992)

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DO Record at Beacon Key (8/27 – 10/27/1992)

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WQ at BCB ( ) and BK ( )

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Phytoplankton Densities (cells/L)

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Cumulative Percent Mortality

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Reproductive Condition from Both Deployments

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Tampa Bay: Laboratory Studies

  • Bay scallop responses to low DO at

several temperature : salinity combinations (for 2 days)

– DO: 1 – 5 mg/L – Temp: 25 – 35o C – Salinity: 15 – 35 ppt

  • Returned to normoxic conditions and
  • bserved latent mortality
  • Measured “escape response”
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Laboratory Results

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Impacts of Karenia brevis on early life stages of Florida populations of bay scallop

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Bay scallop larvae

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84 88 92 96 100 Control W-10 L-10 W-100 L-100 W-1,000 L-1,000 Treatment

a a a a a b b S u r v iv a l (% )

Survival of 3-day old bay scallop larvae exposed to K. brevis and its toxins

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Survival of 7-day old bay scallop larvae exposed to K. brevis and its toxins

20 40 60 80 100 Control 10 100 1,000 5,000 Karenia brevis (cells . ml-1)

*

S u r v iv a l

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Conclusion from larval paper:

“Special attention should be paid to blooms of K. brevis where these shellfish occur naturally or where aquaculture and restoration activities are either ongoing or planned.”

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Juvenile bay scallops

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Clearance rate of juvenile bay scallops exposed to K. brevis

2 4 6 8 10 12 14 Control Whole-10 Lysed-10 Whole-100 Lysed-100 Whole-1,000 Lysed-1,000 Treatment

a a a b b c b,c

Clearance Rate (ml . hr-1 . mg dry wt-1)

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Clearance rate of juvenile scallops exposed to whole K.brevis under flow-through conditions

1 2 3 4 5 Day 1 (PM) Day 2 (AM) Day 2 (PM) Day 3 (AM) Day 3 (PM) Day/Time

Control 100 cells/ml 1,000 cells/ml Clearance Rate (ml

. hr-1 . mg dry wt-1)

a a a a a b b b b b b b b b c

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Clearance rate of juvenile scallops exposed to lysed K.brevis under flow-through conditions

1 2 3 4 Day 1 (AM) Day 1 (PM) Day 2 (AM) Day 2 (PM) Day/Time Control 100 cells/ml 1,000 cells/ml Clearance Rate (ml

. hr-1 . mg dry wt-1)

a a b a a a b b b b b c

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Conclusion from juvenile paper:

“The prospect for recovery of bay scallop populations in Florida estuaries where they were once abundant may be hampered by recurring blooms of K. brevis.”

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Optimal Ranges for Florida Bay Scallops

WATER QUALITY PARAMETER TARGET Temperature (Bottom) 25 – 30o ideal; not to exceed 32o for prolonged periods Salinity (Bottom) Greater than 20 ppt (24 – 30 optimal) DO (Bottom) Not less than 2 mg/L for less than 2 hours Turbidity 5 – 10 NTUs Total Suspended Solids Less than 40 mg/L TSS/VSS Ratio Greater than 1.282 (inorganic C % of seston < 78%) Chlorophyll a 5 – 10 μg/L Phytoplankton Density: less than 5 x 106 cells/L; Species; blooms harmful; Karenia breve fatal. Seagrass Thalassia/Syringodium mix ideal. Density: > 75 shoots/m2; Continuous seagrass beds preferred.