Population Connectivity and Management of an Emerging Commercial Fishery Crow White ESM 242 ProjectMay 31, 2007.

Slides:



Advertisements
Similar presentations
Population Dynamics Wildlife Management.
Advertisements

KELP-SEA URCHIN-FISHERMEN DYNAMICS: IMPLICATIONS FOR SMALL-SCALE FISHERIES MANAGEMENT Nicolas Gutierrez SAFS - UW R Hilborn, AE Punt, LW Botsford, D Armstrong,
Renewable Common-Pool Resources: Fisheries and Other Commercially Valuable Species Chapter 14.
WHERE IS F3 IN MODELING LARVAL DISPERSAL? Satoshi Mitarai, David Siegel University of California, Santa Barbara, CA Kraig Winters Scripps Institution of.
Population dynamics Zoo 511 Ecology of Fishes.
Are the apparent rapid declines in top pelagic predators real? Mark Maunder, Shelton Harley, Mike Hinton, and others IATTC.
Economic efficiency criteria n Static efficiency – Maximize net benefits of one optimal rotation n Dynamic efficiency – Maximize net benefits from continuous.
Population Genetics Kellet’s whelk Kelletia kelletii mtDNA COI & 11 microsatellite markers 28 sampling sites across entire range larvae in each capsule.
1 1 Per Sandberg and Sigurd Tjelmeland Harvest rules and recovery strategies The case of Norwegian spring spawning herring.
Amanda Luna Mera ECL 212B H OW TO GET THERE FROM HERE : E COLOGICAL AND E CONOMIC DYNAMIC OF E COSYSTEM S ERVICE P ROVISION S ANCHIRICO AND S PRINGBORN,
Return on Investment for Lobster (Homarus americanus) Enhancement Initiatives in Atlantic Canada By Marcel LeBreton, Economist, EcoTec Consultants Michel.
1 Open access resource economics Why the free market fails to protect resources.
Marine reserves and fishery profit: practical designs offer optimal solutions. Crow White, Bruce Kendall, Dave Siegel, and Chris Costello University of.
FISHING FOR PROFIT, NOT FISH: AN ECONOMIC ASSESSMENT OF MARINE RESERVE EFFECTS ON FISHERIES Crow White, Bruce Kendall, Dave Siegel, and Chris Costello.
17 cm 6 mm Kellet’s whelk, Kelletia kelletii Habitat: Rocky reef/kelp forests. Partial migration offshore during winter? Carnivorous predator and scavenger.
Marine reserves and fishery profit: practical designs offer optimal solutions. Crow White, Bruce Kendall, Dave Siegel, and Chris Costello University of.
Artificial Population Regulation n For regulation of populations n For commercial harvest n Maximum Sustained Yield (MSY) – Based on the logistic equation:
Income Targeting and the Evolution of a Fishery John Lynham and David Siegel F-cubed meeting, Jan. 24 th, 2007.
Population Dynamics in a Stirred, not Mixed, Ocean Bruce Kendall, David Siegel, Christopher Costello, Stephen Gaines, Ray Hilborn, Robert Warner, Kraig.
Examining the interaction of density dependence and stochastic dispersal over several life history scenarios Heather Berkley Bruce Kendall David Siegel.
FISHING FOR PROFIT, NOT FISH: AN ECONOMIC ASSESSMENT OF MARINE RESERVE EFFECTS ON FISHERIES Crow White, Bruce Kendall, Dave Siegel, and Chris Costello.
17 cm 6 mm. 17 cm 6 mm Kellet’s whelk, Kelletia kelletii Habitat: Rocky reef/kelp forests. Partial migration offshore during winter? Carnivorous predator.
Marine reserve spacing and fishery yield: practical designs offer optimal solutions. Crow White, Bruce Kendall, Dave Siegel, and Chris Costello University.
ERE7: Renewable Resources Fisheries Growth rates in biological resources Steady-state harvest –Perfect market –Open access Dynamic harvesting Policy intervention.
Harvesting stochastic, spatially connected fisheries Christopher Costello (UCSB) Stephen Polasky (UMN) F3 All-Hands-On July 12, 2006 Santa Barbara, CA.
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.
“Fishing” Actually, coupled Flow, Fish and Fishing.
Economics, Density Dependence and the Efficacy of Marine Reserves Crow White Ph.D. Chapter.
Economics of Biotic Resources Ecosystem Structure and Function.
Inherent Uncertainties in Nearshore Fisheries: The Biocomplexity of Flow, Fish and Fishing Dave Siegel 1, Satoshi Mitarai 1, Crow White 1, Heather Berkley.
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.
Spatial and Temporal Patterns in Modeling Marine Fisheries Heather Berkley.
Fishing in a stirred ocean: sustainable harvest can increase spatial variation in fish populations Heather Berkley Bruce Kendall David Siegel.
Examining the interaction of density dependence and stochastic dispersal over several life history scenarios Heather Berkley Bruce Kendall David Siegel.
Flow, fish, and fishing — F 3 Understanding complex interactions of a nearshore ocean ecosystem: Southern California Bight case study.
Chapter 21 Profit Maximization 21-1 Copyright  2002 by The McGraw-Hill Companies, Inc. All rights reserved.
Opportunity Engineering Harry Larsen The Boeing Company SCEA 2000 Conference.
Renewable Common-Pool Resources: Fisheries and Other Commercially Valuable Species.
Material for Week 2: Optimization Techniques Problem 3: Interest rate (i) = 15%
Copyright © 2009 Pearson Addison-Wesley. All rights reserved. Chapter 14 Renewable Common- Pool Resources: Fisheries and Other Commercially Valuable Species.
Status of Lake Trout in the Main Basin of Lake Huron: A Summary of (SCAA) Models and Projections Aaron Woldt--MDNR Alpena.
Spatial management of renewable resources under uncertainty Preliminary results on the economics of coupled Flow, Fish and Fishing Christopher Costello*
Fishery Economics The role of economics in fishery regulation.
Harvesting and viability
Economic impacts of changes in fish population dynamics: the role of the fishermen’s behavior Dipl.-Geogr. Peter Michael Link, BA Research Unit Sustainability.
Flow, Fish and Fishing Dave Siegel, Chris Costello, Steve Gaines, Bruce Kendall, Satoshi Mitarai & Bob Warner [UCSB] Ray Hilborn [UW] Steve Polasky [UMn]
Santa Barbara Coastal LTER & California’s Marine Protected Areas Dave Siegel University of California, Santa Barbara Santa Barbara Coastal LTER.
Fisheries 101: Modeling and assessments to achieve sustainability Training Module July 2013.
Population Ecology. Population Def. a group of individuals of a __________ species living in the same area Characteristics of a popl’n 1)Size 2)Density.
POPULATION DYNAMICS Zoo 511 Ecology of Fishes 2009.
Hydrodynamic Connectivity in Marine Population Dynamics Satoshi Mitarai 1, David A. Siegel 1, Bruce E. Kendall 1, Robert R. Warner 1, Steven D. Gaines.
Evaluation of harvest control rules (HCRs): simple vs. complex strategies Dorothy Housholder Harvest Control Rules Workshop Bergen, Norway September 14,
Optimal continuous natural resource extraction with increasing risk in prices and stock dynamics Professor Dr Peter Lohmander
Chapter 14 Renewable Common-Pool Resources: Fisheries and Other Commercially Valuable Species.
1.  exists when a single firm is the sole producer of a product for which there are no close substitutes. 2.
Copyright © 2009 Pearson Addison-Wesley. All rights reserved.
Economics of Biotic Resources Ecosystem Structure and Function.
Could spatial management of sea urchins increase fishery profits? Sarah Teck, Nick Shears, Sarah Rathbone, Steve Gaines Department of Ecology, Evolution,
EBM: Control Freaks Model Zero: Two interacting species and a regulator who is informationally challenged.
Retrospective bioeconomic analysis of Fraser River sockeye salmon fisheries management Dale Marsden, Steve Martell and Rashid Sumaila Fisheries Economics.
KELLET’S WHELK Kelletia kelletii
Copyright © 2009 Pearson Addison-Wesley. All rights reserved.
Population Dynamics Chapter 52.
Copyright © 2009 Pearson Addison-Wesley. All rights reserved.
Beverton and Holt’s yield per Recruit Model
Renewable Common-Pool Resources: Fisheries and Other Commercially Valuable Species Chapter 14.
Presentation transcript:

Population Connectivity and Management of an Emerging Commercial Fishery Crow White ESM 242 ProjectMay 31, 2007

Adult (15 cm) Recruits Kellet’s whelk Kelletia kelletii

Focus of developing fishery Sold to US domestic Asian market (mostly in LA) Mean price = $1.43/kg = ~$0.15/whelk Aseltine-Neilson et al. 2006

Caught as by-catch by commercial trap fishermen

Research questions:  What is the optimal harvest path that maximizes net present value of the Kellet’s whelk fishery?  Short-term.  Long-term.  How do they differ?

SBA NCI Focus on Santa Barbara area Two patches: SBA: Santa Barbara mainland NCI: Northern Channel Islands Patches differ with respect to: Habitat area, stock size & density Intra- and inter-patch dispersal dynamics Protection in reserves Santa Barbara

EQUATION OF MOTION (patch A): Adult stock [mt]Growth rate“Connectivity” = probability of dispersal Harvest [mt]Annual natural mortality rate Density dependent recruitment K = kelp [km2] Juvenile mortality t = time in years Tj = time until reproductively mature = age of legal size for fishery

CONSTRAINTS: Harvest in a patch must be equal or greater than zero, as well as equal or less than the current stock in that patch In Northern Channel Islands patch harvest may not reduce stock below 20% of its virgin size

12 reserves constituting ~20% of the NCI coastline

EQUATION OF MOTION (patch A): Adult stock [mt]Growth rate“Connectivity” = probability of dispersal Harvest [mt]Annual natural mortality rate Density dependent recruitment K = kelp [km2] Juvenile mortality t = time in years Tj = time until reproductively mature = age of legal size for fishery

SBA NCI Thanks Mike!

(N = 4) Pattern supported by lobster/Kellet’s whelk fisherman (John Wilson, per. comm. 16 May 2007)

Protected in reserves

EQUATION OF MOTION (patch A): Adult stock [mt]Growth rate“Connectivity” = probability of dispersal Harvest [mt]Annual natural mortality rate Density dependent recruitment K = kelp [km2] Juvenile mortality t = time in years Tj = time until reproductively mature = age of legal size for fishery

Mean size (n = 1000+) m = 1/mean age = Tj = ~6 years Annual natural mortality rate: Time until mature: Mature: (Growth data from D. Zacherl 2006 unpub. Res.)

EQUATION OF MOTION (patch A): Adult stock [mt]Growth rate“Connectivity” = probability of dispersal Harvest [mt]Annual natural mortality rate Density dependent recruitment K = kelp [km2] Juvenile mortality t = time in years Tj = time until reproductively mature = age of legal size for fishery

Kellet’s whelk, Kelletia kelletii larvae per egg capsule

Density dependence coefficient Given each patch is a closed system and T j = 1: N* = virgin carrying capacity.

EQUATION OF MOTION (patch A): Adult stock [mt]Growth rate“Connectivity” = probability of dispersal Harvest [mt]Annual natural mortality rate Density dependent recruitment K = kelp [km2] Juvenile mortality t = time in years Tj = time until reproductively mature = age of legal size for fishery

C source-destination: C SBA-SBA = 0.15 C SBA-NCI = 0.34 C NCI-NCI = 0.35 C NCI-SBA = 0.27 Gastropod larva K. kelletia settler (OIPL 2007) (Koch 2006) SBA NCI Thanks James!

Of the total number of settlers arriving at a patch: Santa Barbara AreaNorthern Channel Islands SBANCI Closed system:

Economics:  Revenue based on demand curve:  revenue(t) = choke price – (Harvest[t])(slope)  Cost based on stock effect:  cost(t) = θ / stock density  π(t) = (revenue[t] – cost[t])(1 – r)^-t  r = discount rate = 0.05 ∫

Choke price = max(Price [ ]) All whelks in system Profit calculated at end of each year’s harvest

mr = mc = θ / density, when density = 0.1*min(SBA* or NCI*)

mr, given supply = 1 mt Marginal profit calculated during harvest

Optimization procedure  Short-term: 40 years of harvest  Let un-harvested system equilibrate  Search for optimal harvest path: employ constrained nonlinear optimization function (derivative-based algorithm) in program Matlab.  Goal: find optimal H that maximizes NPV = ∑ π(t)  Long-term: Steady state (t → ∞)  Iterative exploration of all combinations of constant escapement (A – H ≈ 0 – 100%) in each patch.  run until system equilibrates  Goal: identify escapement combination that maximizes π at t = final.

Short-term (40-year) optimal harvest path

Harvest path is variable and different in the two patches

Higher Lower

Initial spike in harvest

Harvest limited by NCI reserve constraint

Harvest until mr = mc

Harvest path is semi-cyclic: due to delayed development?

NPV = ∑ π(t) = $1,279,900 ~$32,000/year

10,000 simulations: NPV H* H* - (v/2)(H*)H* + (v/2)(H*) H(t) = H* + U[-v/2, +v/2](H*)

10,000 simulations: 90% NPV H* H* - (v/2)(H*)H* + (v/2)(H*) NPV H(t) = H* + U[-v/2, +v/2](H*)

Long-term optimal harvest

Harvest everything

$68,067/year

Harvest everything $68,067/year 40-year horizon and r = 0.05: ~$31,000/year

Harvest everything $68,067/year 40-year horizon and r = 0.05: ~$31,000/year

Harvest everything $68,067/year 40-year horizon and r = 0.05: ~$31,000/year

Harvest everything 90%

Harvest everything Plenty Room for uncertainty: Little

90% NCI reserve constraint Harvest everything NCI used as a source, regardless of regulation!

Future research: 1.Improve accuracy in parameter estimates (e.g., λ, population density) and re-run analysis. 1.Relevance of NCI reserve constraint? 2.Incorporate known variability (e.g., connectivity across years) and uncertainty (e.g., in λ and form of density dependence function) into analysis. 3.Apply model to a variety of systems characterized by different levels of connectivity.

Currents Oceanographic boundaries (Gaylord & Gaines 2000)

Central CA Southern CA US Mexico Borders dividing fishery management jurisdictions Is cooperation in cross- border management part of the optimal solution?

Thank you!

10,000 simulations: 90% net present value H* H* - U[1-v,1+v](H*) H* + U[1-v,1+v](H*)

Southern hemisphere cetaceans (Hilborn et al. 2003)

“Rapid worldwide depletion of predatory fish” (Myers & Worm 2003)

Mean size (n = 1000+) m = 1/mean age = Annual natural mortality rate:

Excellent for lawn art (match gnomes beautifully!)

Thank you!