Geomorphology of grouper and snapper spawning aggregation sites in the Upper Florida Keys, USA

Similar documents
Effective multi-agency collaboration improves spatial monitoring and planning in the Florida Keys

Biogeographic Assessment of Florida Keys National Marine Sanctuary

Fish Aggregations in the Florida Keys

Acoustic signatures of the seafloor: tools for predicting grouper habitat

Domain (island) wide estimates of mutton snapper (Lutjanus analis) abundance for three US Caribbean Islands based on habitat-derived densities

Geomorphometric Analysis of Nassau Grouper Spawning Aggregation Sites in Belize and the Cayman Islands

1. What are the scientific names of red snapper, gag grouper, and scamp grouper? 2. What families do red snapper, gag grouper, and scamp belong to?

Towards Sustainable Multispecies Fisheries in the Florida Coral Reef Ecosystem

Modeling effects of fishing closures in the Western Florida Shelf

Improving fishermen awareness to reduce the presence of lobster traps in MPAs of the Florida Keys. Gabrielle Renchen & Tom Matthews

DESCRIPTION OF REEF FISH SPAWNING AGGREGATIONS AT MONA ISLAND PUERTO RICO

South Atlantic proposed MPAs: : three years of pre- closure data on habitat and fish assemblages

Artificial Reef Program Biological Monitoring Update

Spawning Aggregation Evaluation. Utila January February 2009

Fisheries of the Caribbean, Gulf of Mexico, and South Atlantic; Reef Fish Fishery of Puerto Rico and the U.S. Virgin Islands;

Experimental Studies of Factors Affecting Coral Recruitment in La Parguera, Puerto Rico. Alina Szmant (UNCW) and Ernesto Weil (RUM)

VII. Marine debris distribution

Billing Code: P. Fisheries of the Caribbean, Gulf of Mexico, and South Atlantic;

BERMUDA GOVERNMENT Ministry of Health, Seniors and Environment Department of Environmental Protection

SEDAR 10 DW- 08. REVIEW OF TAGGING DATA FOR GAG GROUPER (Mycteroperca microlepis) FROM THE SOUTHEASTERN GULF OF MEXICO REGION

ESSENTIAL FISH HABITAT HABITAT AREAS OF PARTICULAR CONCERN (EFH-HAPC) AND CORAL HABITAT AREAS OF PARTICULAR CONCERN (C-HAPC)

Florida Fish and Wildlife Conservation Commission (FWC)

Glover s Reef Marine Reserve Long-term Atoll Monitoring Program (LAMP)

SCDNR Research and Monitoring: Habitat Needs of Different Life History Stages of Managed Reef Species

Essential Fish Habitat Description Atlantic cod (Gadus morhua)

Islands in the Stream: A Concept for the Gulf of Mexico

Bottomfish Habitat and Restricted Fishing Area Analysis

Evolution of Deepwater Coral Protection in the Southeast U.S

Flower Garden Banks National Marine Sanctuary Management Plan Revision

WALTON COUNTY NRDA ARTIFICIAL REEF PROGRAM

Essential Fish Habitat: An overview of the consultation requirement for the American Association of Port Authorities

Challenges in determining water surface in airborne LiDAR topobathymetry. Amar Nayegandhi, Dewberry 15 th Annual JALBTCX Workshop, June 11 th 2014

Are the Coral Reef Finfish Fisheries of South Florida Sustainable?

MAHS Field School 2018 Pickles Reef Florida Keys National Marine Sanctuary

VIII. Marine Debris. Background

Acoustic tagging: abundance indices and habitat use Juvenile southern bluefin tuna in Western Australia

Eastern Shore Islands Area of Interest Community Newsletter

Unless otherwise noted, images throughout the presentation are by FWC.

Utilizing Vessel Based Mobile LiDAR & Bathymetry Survey Techniques for Survey of Four Southern California Breakwaters

PUBLIC HEARING GUIDE 10/4/12

Reef Fish Amendment 32 Gag and Red Grouper

NSUWorks. Nova Southeastern University. Kirk Kilfoyle Nova Southeastern University Oceanographic Center

Recreational - Charter Fishing Working Group. Recommendations to the Sanctuary Advisory Council

/ Advice May 2011

Assessment of the Introduced Lionfish in Everglades and Dry Tortugas National Parks

Teachers copy. 1. What are the scientific names of red snapper, gag grouper, and scamp grouper?

Updated landings information for the commercial fisheries in Puerto Rico with emphasis on silk and queen snapper and parrotfish fisheries

VIDEO TRANSCRIPT. A Proposal to Expand the Flower Garden Banks National Marine Sanctuary An interview with Sanctuary Superintendent, G.P.

Evaluation of the Klein HydroChart 3500 Interferometric Bathymetry Sonar for NOAA Sea Floor Mapping

Deep-sea coral protection zones and management measures

Monetisation of sustainable business models for Satellite Derived Bathymetry

Marine Recreational Information Program Transition to Improved Survey Designs

Minimum Stock Size Threshold (MSST) for reef fish stocks with low natural mortality

Deep-sea corals of the USA: Surveys, maps, & models for exploration and management

Fishing Volusia County s Artificial Reefs

Essential Fish Habitat Description White hake (Urophycis tenuis)

Field Protocol for Monitoring Coral Reef Fisheries Resources in Belize

Synopsis. Site Characterization for Biscayne National Park: Assessment of Fisheries Resources and Habitats

Angler Heterogeneity and Species- Specific Demand for Recreational Fishing in the Southeast United States

Implementing the Dry Tortugas National Park. Research Natural Area Science Plan The 5-Year Report

Methods and Lessons Learned from a Fisheries- Independent Reef Fish Sampling Program in the Florida Keys, USA

Working Group Meeting Summary

National Oceanic and Atmospheric Administration (NOAA)/ Mulberry Phosphate Trustee Council September 12, 2013

Case Study 3. Case Study 3: Cebu Island, Philippines MPA Network 10

SOUTH ATLANTIC FISHERY MANAGEMENT COUNCIL

National Marine Fisheries Service, Habitat Conservation Division:

Assessment of Artificial Reefs Impacted by Hurricane Michael

UNDERWATER ARCHAEOLOGY Pickles Reef Florida Keys National Marine Sanctuary

OECS Regional Engineering Workshop September 29 October 3, 2014

An Overview of Methods for Estimating Absolute Abundance of Red Snapper in the Gulf of Mexico

East Central Florida Region Matt Culver, Brevard County James Gray, Indian River County Jim Oppenbourn, St. Lucie County Kathy Fitzpatrick, Martin

Assessing the Accuracy of High Spatial Resolution Effort Data

Barotrauma in Atlantic Coast Fisheries. Chip Collier March 2011

Zooplankton community structure in the northern Gulf of Mexico: Implications for ecosystem management

Figure 4, Photo mosaic taken on February 14 about an hour before sunset near low tide.

Characterizing the Fish Assemblages of Cordell Bank National Marine Sanctuary

An IOOS Operational Wave Observation Plan Supported by NOAA IOOS Program & USACE

Information needs for resource management in and around Florida Bay

August 3, Prepared by Rob Cheshire 1 & Joe O Hop 2. Center for Coastal Fisheries and Habitat Research Beaufort, NC

Examples of Carter Corrected DBDB-V Applied to Acoustic Propagation Modeling

Summary of current information available on Coastal Pelagic Species with emphasis on Northern Anchovy

Blue Star Fishing Guides

and found that there exist a significant overlap between the billfish resources and the exploitation activities targeting tunas and mahi mahi.

Semi-Annual Progress Report for: June 1, November 30, 2004

Essential Fish Habitat Description Atlantic herring (Clupea harengus)

A PHYSICAL AND BIOLOGICAL SURVEY OF THE MID-REACH MITIGATION REEF SET NUMBER 1

THE POLARIMETRIC CHARACTERISTICS OF BOTTOM TOPOGRAPHY RELATED FEATURES ON SAR IMAGES

ABSTRACT INTRODUCTION

Eglin Air Force Base, FL

United Nations Environment Programme

Coral Habitat Areas Considered for Management in the Gulf of Mexico

Severe Winds Due To Mountain Waves Along the Western Foothills of the Southern Appalachian Mountains

Ecological Interactions in Coastal Marine Ecosystems: Rock Lobster

Florida s Artificial Reef Monitoring Efforts

GFCM - SAC-SCESS-SCMEE-SCSA Transversal Workshop on Spatial Based Fishery Management. 6-8 Feb 2012

Red Snapper distribution on natural habitats and artificial structures in the northern Gulf of Mexico

Oceanic Society Reef Research Team: Nicole Crane, Avigdor Abelson, Peter Nelson, Giacomo Bernardi, Michelle Paddack, Kate Crosman

Citizen Science Based Survey GBR Far North Dive Trip 2016 April 18-26

CHARACTERIZING THE BEACH MORPHOLOGY OF SAN SALVADOR, BAHAMAS

Seagrass surveys must be conducted between the dates of April 1 st and October 31 st with the following exceptions:

Transcription:

Geomorphology of grouper and snapper spawning aggregation sites in the Upper Florida Keys, USA Art Gleason, Pamela Reid Division of Marine Geology and Geophysics University of Miami / Rosenstiel School of Marine and Atmospheric Science Todd Kellison National Marine Fisheries Service Southeast Fisheries Science Center

Florida Keys National Marine Sanctuary (FKNMS) An innovative network of marine zoning includes 25 no-take areas FKNMS established 1990 Dry Tortugas No-take area approved 2001 23 No-take SPAs approved 1997

Black Grouper Census at Carysfort Reef Carysfort SPA (July 1997)` North Carysfort (emergent) South Carysfort (emergent) Mycteroperca bonaci (black grouper) 1500 m Jiangang Luo photo Eklund et al. (2000) Depth 2-5 m 20 m 150 m

Black Grouper Census at Carysfort Reef Carysfort SPA (July 1997) Eklund et al. (2000) 1500 m M. bonaci counts (all seasons 1997-2002) X 0 1-10 11-20 21-30 31-40 40-70

Black Grouper Census at Carysfort Reef Carysfort SPA (July 1997) Eklund et al. (2000) 1500 m M. bonaci counts (Jan & Dec 1998) X 0 1-10 11-20 21-30 31-40 40-70

A Problem...

One reason for this: no habitat maps > 20 m. 1 km 1994 on: high abundance of groupers 1998: 100 Black Groupers! 1997: Carysfort SPA Airphoto Classification Hardbottom Seagrass Patch Reefs Bare Sediment

Lack of habitat data for deep / turbid water > 50% of FKNMS!

Acoustic survey (2003) with QTC-View V 1 km

SPA border Modern (Holocene) Reef: too shallow to survey Carysfort survey results A 30 m Outlier reef 30 m ridge 36 m ridge 50 m Outlier reef Shaded relief from bathymetry Seabed type from echo shape Hardbottom (reef) Mixed rock/sediment Sediment B A 30 m Outlier 30 & 36 m ridges 50 m Outlier Aggregation Site B

Carysfort survey results SPA border A Black grouper aggregation site On steepest part of 30 m outlier Inshore exposed 30, 36 m ridges Inshore exposed 50 m outlier Does this pattern hold for other aggregation sites in the Keys? B A Aggregation Site B

Historical aggregation sites Bear Cut: Gag grouper Lutjanus analis (mutton snapper) Jiangang Luo photo Ocean Reef: Mutton Snapper Mycteroperca bonaci (black grouper) 15 km Davis Reef Yellowtail Snapper Carysfort Reef: Black Grouper Watsons Reef: Black Grouper Yellowtail Snapper Mutton Snapper Jiangang Luo photo Lutjanus chrysurus (yellowtail snapper) Jiangang Luo photo

Watsons & Carysfort viewed together Black grouper & Yellowtail snapper Offshore steepest part of 30 m outlier Upstream Watsons of exposed reef (new 36 m this ridge slide) Downstream of patch reefs Black grouper (from earlier slide) On steepest part of 30 m outlier Inshore Carysfort exposed (already 30, seen 36 earlier) m ridges Inshore exposed 50 m outlier 30 m ridge 30 m Outlier reef 36 m ridge 50 m Outlier reef Mutton Snapper: Offshore steepest part of 30 m outlier On partially exposed face of 50 m outlier 12 km

Seabed type complements bathymetry Looks flat, but is really high-rugosity patch reefs Looks promising, but is really barren sediment slope 12 km

SPA border Davis Yellowtail snapper On steepest part of 30 m outlier Inshore of unexposed 30 m ridge, 50 m outlier 30 m Outlier reef 30 m ridge 50 m Outlier reef

Ocean Reef Mutton snapper Offshore steepest part of 30 m outlier On exposed 30 m ridge Inshore exposed 36 m ridge, 50 m outlier 30 m Outlier reef 30 m ridge 36 m ridge 50 m Outlier reef

Bear Cut Gag grouper Offshore steep part of 30 m outlier Downstream unexposed 30 / 36 m ridge 30 m Outlier reef 30/36 m ridge (?)

Upper Keys Aggregation Sites Model Original Hypothesis (Based on Carysfort) Aggregation sites expected at a point meeting three conditions : 1) On steepest part of 30 m outlier 2) Inshore exposed 30, 36 m ridges 3) Inshore exposed 50 m outlier 30 m Outlier reef Side view (depth profile) 30 / 36 m ridges 50 m Outlier reef Top view (depth contours)

Upper Keys Aggregation Sites Model Revised Model (Based on observations at additional Upper Keys sites) Aggregation sites expected within a band meeting three conditions: 1) On face or offshore of steepest part of 30 m outlier 2) Within 100 m (along shore) of exposed 30 / 36 m ridge 3) On face of or inshore exposed 50 m outlier How well do sites fit the revised model? Site 1 2 3 Carysfort (Black) Y Y Y Watsons (Black and Yellowtail) Y Y Partial Davis (Yellowtail) Y N N Watsons (Mutton) Y Y Partial Ocean Reef (Mutton) Y Y Y Bear Cut (Gag) Y Maybe N

Relevance to Caribbean 200 km 5km

Macintyre 1972: Shelf edge reefs on 40m terrace Eastern Caribbean Islands Anguilla St. John Montserrat Barbados Grenadines On all plots: a) both axes in meters (vertical exaggeration = 10x) b) red line marks 50 m depth

Summary Outlier reefs are: critical habitat in the Upper Fl Keys critical habitat elsewhere (probably) too deep to survey with imagery possible to survey with acoustics (or lidar maybe) Deep water survey needed when considering MPA boundaries: We don t want another Carysfort. Benefits of single beam Inexpensive Retrieves substrate type, not just bathymetry

Acknowledgements Funding from NOAA CRCP and ONR SPAG local knowledge from Roberto Torres Diving and boat ops support: Dave McClellan, Mark Miller, Jack Javech, Leah Harman, Sean Cimulluca, Doug Harper, Joe Contillo, Heather Balchowsky, Jen Schull, Neil Baertlein Anne-Marie Eklund initiated this project