Could spatial management of sea urchins increase fishery profits? Sarah Teck, Nick Shears, Sarah Rathbone, Steve Gaines Department of Ecology, Evolution,

Slides:

Advertisements

Similar presentations

KELP-SEA URCHIN-FISHERMEN DYNAMICS: IMPLICATIONS FOR SMALL-SCALE FISHERIES MANAGEMENT Nicolas Gutierrez SAFS - UW R Hilborn, AE Punt, LW Botsford, D Armstrong,

Advertisements

Yakama Nation Pacific Lamprey Recovery Project Core Data And Monitoring Framework.

A life history framework to understand production of juvenile steelhead in freshwater applied to the John Day River, Oregon Jason Dunham, USGS Forest and.

Coastal Communities and Marine Resources David Whitaker Department of Natural Resources.

ODFW Marine Data Collection Efforts Northwest Area Committee Meeting November 2011 David Fox Oregon Department of Fish & Wildlife Marine Resources Program.

ROMS Modeling for Marine Protected Area (MPA) Connectivity Satoshi Mitarai, Dave Siegel, James Watson (UCSB) Charles Dong & Jim McWilliams (UCLA) A biocomplexity.

California’s Gold: Ensuring a profitable and sustainable sea urchin fishery Sarah Teck 14 April 2011 CINMS J. Maassen.

 Homework #8 Due Thursday  Quiz #4 Thursday Nov. 17 th  Homework #9 Thursday Nov. 17 th  Group Outline due Thursday Nov. 17th  Exam #4 Dec. 1st.

SIO 286 January 11, 2011 Answers to questions - collect Field trip waivers Turtle trip feedback Next week refreshments following class; volunteers.

Marine reserves and fishery profit: practical designs offer optimal solutions. Crow White, Bruce Kendall, Dave Siegel, and Chris Costello University of.

Giant Kelp Canopy Cover and Biomass from High Resolution SPOT Imagery for the Santa Barbara Channel Kyle C Cavanaugh, David A Siegel, Brian P Kinlan, Dan.

Income Targeting and the Evolution of a Fishery John Lynham and David Siegel F-cubed meeting, Jan. 24 th, 2007.

Spatio-temporal Stochastic Simulation of Connectivity Matrices from Lagrangian Ocean Models.

Marine reserve spacing and fishery yield: practical designs offer optimal solutions. Crow White, Bruce Kendall, Dave Siegel, and Chris Costello University.

Flow, Fish and Fishing: Building Spatial Fishing Scenarios Dave Siegel, James Watson, Chris Costello, Crow White, Satoshi Mitarai, Dan Kaffine, Will White,

Spatial fisheries management in practice: an example.

Inherent Uncertainties in Nearshore Fisheries: The Biocomplexity of Flow, Fish and Fishing Dave Siegel 1, Satoshi Mitarai 1, Crow White 1, Heather Berkley.

Modeling fishermen behavior in the Santa Barbara Channel Islands geog.Mike & econ.John

Will spatial property rights lead to ocean conservation? Christopher Costello Bren School – UC Santa Barbara California and the World Ocean September 9,

Image: Michael Robinson Geography Department UC Santa Barbara Fisherman Behavior and Fishery Management: A Cooperative Investigation.

Quantifying Connectivity in the Coastal Ocean With Application to the Southern California Bight Satoshi Mitarai, Dave Siegel, James Watson (UCSB) Charles.

Spatial Bioeconomics under Uncertainty (with Application) Christopher Costello* September, 2007 American Fisheries Society Annual Meeting San Francisco,

Fishing in a stirred ocean: sustainable harvest can increase spatial variation in fish populations Heather Berkley Bruce Kendall, David Siegel, Christopher.

An overview of CALobster (California Lobster Collaborative) Matt Kay – UC Santa Barbara.

Environmental Drivers & Biological Sources of Inter-annual Variation in Net Primary Production by Giant Kelp Dan Reed Collaborators: Mike Anghera, Katie.

Kelp-Sea Urchin-Fishermen: a Spatially Explicit Individual-Based Model Nicolas Gutierrez and Ray Hilborn School of Aquatic and Fishery Sciences University.

Can property rights solve fisheries collapse? Christopher Costello* Associate Professor – Resource Economics Bren School Advisory Board Address: April.

Reserve design There’s a lot of crap out there We are in a position to inform how to do this intelligently.

 Homework #8 due Wednesday  Homework #9 due next Wednesday  Quiz #4 Wednesday Nov. 14 th  Group Outline due Wed. Nov. 14th.

MARINE PROTECTED AREAS. What Are MPAs? – Marine Protected Areas (MPAs) are geographic areas designated to protect or conserve marine life and habitat.

Andrew Rassweiler 1, Chris Costello 1, Dave Siegel 1, Giulio De Leo 2, Fiorenza Micheli 3, Andrew Rosenberg University of California Santa Barbara.

Biodiversity Environmental Science Notes Series. What is Biodiversity? Species Richness is another term for biodiversity Density is an important factor.

Nearshore fish communities response to habitat variability Terril P. Efird School of Fisheries and Ocean Sciences University of Alaska Fairbanks.

Spatial Fisheries Values in the Gulf of Alaska Matthew Berman Institute of Social and Economic Research University of Alaska Anchorage Ed Gregr Ryan Coatta.

Fishing Food for human consumption – Globally, fish is ~20% of animal protein consumed Animal feed (both aquaculture & livestock) Natural products – Inverts,

Giant Kelp Canopy Cover and Biomass from High Resolution Multispectral Imagery for the Santa Barbara Channel Kyle C Cavanaugh, David A Siegel, Brian P.

Spatial fisheries management for conservation and profitability Christopher Costello* University of California and National Bureau of Economic Research.

Partnership for Interdisciplinary Studies of Coastal Oceans PISCO.

Scales of larval settlement in marine fishes and invertebrates Elizabeth Madin and Robin Pelc November 5, 2004.

Sea Urchin Population Issues in California Kelp Forests Andy Ostrowski Bio 457- Fall 2004.

Kelp Forests BY:MATT BEALE LUCAS SAMUEL AND DESTIN WEBB.

UNIT 8: Fisheries assessments. 2 Fisheries data Why do we need fisheries data? FAO (2005): “Information is critical to EAF. It underpins the formulation.

Fisheries production estimates. Relationship between fisheries yield and primary production estimates.

Biostatistics: Sampling strategies Data collection for fisheries assessment: Monitoring and sampling strategies.

Visualizing Coastal Vulnerability and People for the U.S. National Climate Assessment (NCA) Gregg Verutes, Greg Guannel, Katie Arkema and Spencer Wood.

Santa Barbara Coastal LTER & California’s Marine Protected Areas Dave Siegel University of California, Santa Barbara Santa Barbara Coastal LTER.

Dave Siegel, Kyle Cavanaugh, Brian Kinlan, Dan Reed, Phaedon

Fisheries 101: Modeling and assessments to achieve sustainability Training Module July 2013.

Issues of Scale Both time & space – Time: waves, tides, day, year, ENSO – Space: local, regional, global Set how processes interact Scale invariance.

Steve Gaines Bren School of Environmental Science & Management Sustainable Fisheries Group UC Santa Barbara12 May 2011.

Hydrodynamic Connectivity in Marine Population Dynamics Satoshi Mitarai 1, David A. Siegel 1, Bruce E. Kendall 1, Robert R. Warner 1, Steven D. Gaines.

Channel Islands National Marine Sanctuary: Advancing the Science and Policy of Marine Protected Areas Satie Airame Channel Islands National Marine Sanctuary.

Is the recent Cap Roux Marine Protected Area (France, Var) an efficient tool to sustain professional fisheries ? 8e Forum halieumétrique, La Rochelle,

Scallop Dive (Port Phillip Bay) Fishery Cover photo - PMSS COMMERCIAL SCALLOP DIVE FISHERY - PORT PHILLIP BAY Results of the Fishery-Independent Dive Survey.

Territorial Coral Reef Monitoring Program (TCRMP) Caribbean Fishery Management Council Meeting St. Thomas USVI December 15-16, 2015 Leslie Marie Henderson.

Current Oversights in Marine Reserve Design. MARINE RESERVE DATA BASE 81 studies, 102 measurements Halpern, in press.

NSERC / FFAW Project: Sustainable Fisheries Lobsters in Western Newfoundland: Reproductive Relative to Economic Value 5 November 2010.

Abalone Management in California Presentation to the Fish and Game Commission Mr. Ian Taniguchi and Dr. Laura Rogers-Bennett Department of Fish and Game.

The spatial and temporal consequences of overfishing.

Location Choice and Expected Catch: Determining Causal Structures in Fisherman Travel Behavior Michael Robinson Department of Geography University of California,

Training course in fish stock assessment and fisheries management

PRINCIPLES OF STOCK ASSESSMENT. Aims of stock assessment The overall aim of fisheries science is to provide information to managers on the state and life.

Special Session: Landing Obligation

Environmental and Natural Resource Economics 3rd ed. Jonathan M

IV. Contribution of larval behavior to vertical zonation patterns

Integrating biological components into a spatially explicit, complex economic model for fisheries management evaluations: The North Sea saithe fishery.

Southern California Green Abalone Restoration Project

Integrate modules sustaining our oceans

Chapter 5 Biodiversity, Species Interactions, and Population Control

Presentation transcript:

Could spatial management of sea urchins increase fishery profits? Sarah Teck, Nick Shears, Sarah Rathbone, Steve Gaines Department of Ecology, Evolution, and Marine Biology, University of California Santa Barbara Photo: CINMS Photo: J. Maassen

Santa Barbara San Miguel Santa Rosa Anacapa Santa Cruz Background red sea urchin fishery: –California ~11.2 million lbs. ~$6.1 million –N. Channel Islands ~66% –Port of Santa Barbara ~52% –90% western end Image:

Background seasonal variability in gonad quality influences price ($0.39/lb vs >$1.00/lb) fishermen race to harvest year-round vs. waiting for optimal quality (how much more $ would they make, if they waited?) delaying harvest through spatial property rights, TURF’s (Territorial Use Rights in Fisheries)  fishermen’s profits (also would save time, no need to survey area to fish during suboptimal conditions, just wait for optimal quality)

Background with fished species need to wait for individuals and population growth with urchins also need to wait for seasonal gonad quality first, we need to understand more detailed ecological information on temporal and spatial variability of gonad quality

Background with fished species need to wait for individuals and population growth with urchins also need to wait for seasonal gonad quality first, we need to understand more detailed ecological information on temporal and spatial variability of gonad quality

Santa Barbara San Miguel Santa Rosa Anacapa Santa Cruz Channel Island field sampling

Santa Barbara San Miguel Santa Rosa Anacapa Santa Cruz Red urchin gonad variability over space gonad: somatic index (GSI)

Santa Barbara Port sampling

Red urchin gonad variability over time gonad: somatic index (GSI) Oct ‘08 DecFeb ‘09 MarMayJulAugOct

Red urchin gonad variability over time gonad: somatic index (GSI) Oct ‘08 DecFeb ‘09 MarMayJulAugOct

Red urchin gonad variability over time gonad: somatic index (GSI) Oct ‘08 DecFeb ‘09 MarMayJulAugOct

Red urchin gonad variability over time gonad: somatic index (GSI) Oct ‘08 DecFeb ‘09 MarMayJulAugOct

Red urchin gonad variability over time gonad: somatic index (GSI) Oct ‘08 DecFeb ‘09 MarMayJulAugOct

Red urchin landings Purple urchin abundance 2007

purples compete with reds for kelp not commercially harvested (smaller) form persistent urchin barrens (mostly in the east) long-term monitoring sites deforested by purples ~33% of the time—mostly in the east purple sea urchin

manipulate ecology of a managed area to increase profits  kelp restoration

Long-term ( ) Variation in Kelp and Urchin NPS—KFM data (eastern SCI and Anacapa Island) Biomass (gm -2 ) Density (m -2 ) kelp purple urchins red urchins

Long-term ( ) Variation in Kelp and Urchin NPS—KFM data (eastern SCI and Anacapa Island) Biomass (gm -2 ) Density (m -2 ) kelp purple urchins red urchins

Long-term ( ) Variation in Kelp and Urchin NPS—KFM data (eastern SCI and Anacapa Island) Biomass (gm -2 ) Density (m -2 ) kelp purple urchins red urchins Red urchins have persistently higher biomass inside of the reserves. Reproductive output is ~4 times higher in kelp forests versus urchin barrens

ecological restoration & economic revitalization