The economics of fishery management The role of economics in fishery regulation.

Slides:



Advertisements
Similar presentations
Basic Bioeconomics Model of Fishing
Advertisements

The assumption of maximizing behavior lies at the heart of economic analysis. Firms are assumed to maximize economic profit. Economic profit is the difference.
Renewable Common-Pool Resources: Fisheries and Other Commercially Valuable Species Chapter 14.
NAAFE FORUM: ENSURING FISHERIES BENEFITS FOR ALL GENERATIONS DISCIPLINARY AND PERSONAL PERSPECTIVES ON “ THE FISHERIES PROBLEM ” by James E. Wilen Department.
Individual Transferrable Quotas: New Zealand’s Experience.
Evolving Approaches to Managing Recreational Fisheries Donald Leal The Property and Environment Research Center August 12, 2009 The Gulf of Mexico Fishery.
Public Goods and Common Property Resources. Harcourt, Inc. items and derived items copyright © 2001 by Harcourt, Inc. Characteristics of Goods When thinking.
Fisheries. efficient harvests biology biology economic economic.
Upcoming in Class Homework #8 Due Thursday Quiz #4 Thursday Nov. 17th
Public Goods and Common Property Resources Chapter 11.
Renewable, open-access resources: fisheries
Ecological Impacts of Current Quota Systems Rainer Froese.
The development of the Icelandic fisheries in the post- war era closely followed the path predicted for common property fisheries. They exhibit increasingly.
 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.
 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.
1 Open access resource economics Why the free market fails to protect resources.
Fishery Economics The role of economics in fishery regulation.
Individual Transferable Quotas in the Baltic Sea Herring Fishery: a Socio-bioeconomic Analysis Soile Kulmala, Hanna Peltomäki, Marko Lindroos, Sakari Kuikka.
Fisheries: The steady-state model
Grafton, Squires, and Fox. Private Property and Economic Efficiency: A study of a common-pool resource. B.C. halibut fishery provides a natural experiment.
ERE7: Renewable Resources Fisheries Growth rates in biological resources Steady-state harvest –Perfect market –Open access Dynamic harvesting Policy intervention.
Managing the Fishery How can we regulate the fishery to avoid problems of open access?
Can property rights solve fisheries collapse? Christopher Costello* Associate Professor – Resource Economics Bren School Advisory Board Address: April.
Imperfect Competition and Market Power: Core Concepts Defining Industry Boundaries Barriers to Entry Price: The Fourth Decision Variable Price and Output.
Renewable Resources Reading Perman et al (2nd ed.) Chapters 9 and 10
 Homework #8 due Wednesday  Homework #9 due next Wednesday  Quiz #4 Wednesday Nov. 14 th  Group Outline due Wed. Nov. 14th.
 Homework #8 due today  Homework #9 due next Wednesday  Quiz #4 Wednesday Nov. 14 th  Group Outline due Wed. Nov. 14 th  Exam #4 Wed. Nov 28 th 
Icelandic Fisheries Legislation Development and Experience Presentation November 2005.
Fishery Management Fishing is extractive – Removes choices organisms- “ fine-ing ” – Changes food web structure The human condition provides little incentive.
Your exams: graded, yes, but I forgot them at home.
Economics of Renewable Natural Resources
International (fisheries) agreements and game theory
Renewable Common-Pool Resources: Fisheries and Other Commercially Valuable Species.
Copyright © 2009 Pearson Addison-Wesley. All rights reserved. Chapter 14 Renewable Common- Pool Resources: Fisheries and Other Commercially Valuable Species.
Basic Fisheries Management Theory - Background - Fame workshop on New Developments in Rights-based Fisheries Management: Community Fishing Rights Esbjerg,
Copyright © 2008 Pearson Addison-Wesley. All rights reserved. Chapter 9 Competitive Markets.
Fishery Biology. Fisheries Management n Provide people with a sustained, high, and ever-increasing benefit from their use of aquatic resources n Problems.
May 2000 INTRODUCTION TO BIOECONOMIC MODELS FOR FISHERY - THE SCHAEFER-GORDON MODEL INTRODUCTION TO BIOECONOMIC MODELS FOR FISHERY - THE SCHAEFER-GORDON.
Fishing = Harvesting = Predation Predator-Prey Interaction +- with Humans as Predator Very high-tech hunting- gathering –Fast boats –Sonar, fish finders.
AGEC/FNR 406 LECTURE 27 Fisheries, Part II. Static-efficient sustained yield Gordon model (simplest approach) Goal: determine a catch level that provides.
Fishery Economics The role of economics in fishery regulation.
Exam 2 review. resource economics nonrenewable vs. renewable –maximize pv of net benefit –renewable includes growth functions characterize efficient allocations.
Economics of Fisheries © 2008 by Peter Berck. Economic Issues in Fisheries Present value maximizing fishing rules The open access outcome Regulation by.
PROVISIONS OF H.R SECTION 3: SCIENCE BASED IMPROVEMENTS TO MANAGEMENT [303(a )] Page 3, lines 22-25, Page 4, Page 5, lines 1-9 Paragraph 15 is.
Natural Resource Economics Academic year: Prof. Luca Salvatici Lesson 24: Optimal (harvesting) effort.
Renewable Common-Pool Resources: Fisheries and Other Commercially Valuable Species.
Chapter 14 Renewable Common-Pool Resources: Fisheries and Other Commercially Valuable Species.
The Fishery Resource: Biological and Economic Models Wednesday, April 12.
Copyright © 2009 Pearson Addison-Wesley. All rights reserved.
Fisheries management around the world: elements and implementation Ray Hilborn School of Aquatic and Fishery Sciences University of Washington.
Public Goods and Common Property Resources Chapter 11.
Economics of Fisheries © 2008 by Peter Berck. Economic Issues in Fisheries Present value maximizing fishing rules The open access outcome Regulation by.
Sustaining Aquatic Biodiversity Chapter What Are the Major Threats to Aquatic Biodiversity?  Concept 11-1 Aquatic species are threatened by.
Managing the Fishery How can we regulate the fishery to avoid problems of open access?
Quiz 7. Harvesting strategies and tactics References Hilborn R, Stewart IJ, Branch TA & Jensen OP (2012) Defining trade-offs among conservation, profitability,
Fisheries Management: Principal Methods, Advantages and Disadvantages
Public Goods and Common Resources
Maximum Sustainable Yield & Maximum Economic Yield
Natural resources come in two types
Fisheries Management Scientists study fish stocks to determine estimates of the population count and the reproductive biology of the species This information.
Growth rate (replacement) and size of the fish stock/pool
K. Beadle TURF-Reserves Designing Effective Area- Based Catch Shares.
Copyright © 2009 Pearson Addison-Wesley. All rights reserved.
National Marine Science Centre, Southern Cross University, Australia
National Marine Science Centre, Southern Cross University, Australia
Copyright © 2009 Pearson Addison-Wesley. All rights reserved.
Renewable Common-Pool Resources: Fisheries and Other Commercially Valuable Species Chapter 14.
Growth rate (replacement) and size of the fish stock/pool
How Offshore Fisheries Can Be Both Sustainable and Profitable
The Fishery Resource: Biological and Economic Models
Presentation transcript:

The economics of fishery management The role of economics in fishery regulation

Simple model of fish biology time Biomass (x) x “Carrying Capacity” x MSY Stock that gives “maximum sustainable yield”

Interpreting this curve x Growth rate of population depends on stock size low stock  slow growth high stock  slow growth Also “sustainable yield curve” MSY

Introduce humans Harvest depends on Harvest “effort”, stock size, and technology x kE H x kE L x H H = k*E*x k = technology “catchability” E = effort (e.g. fishing days) x = biomass or stock Harvest for low effort Harvest for high effort

Does stock grow or shrink? If more fish are harvested than grow, population shrinks. If more fish grow than are harvested, population grows. For any given E, what harvest level is just sustainable? Where k*E*x =

“Yield-effort curve” H(E) E Gives sustainable harvest as a function of effort level

Introduce economics Costs of harvesting TC = w*E w is the cost per unit effort Revenues from harvesting TR = p*H(E) p is the price per unit harvest Draw the picture

$ TR=p*H(E) TC=w*E E MC MR $/E E w Rents to the fishery E OA E* Value of fishery maximized at E*. Profits attract entry to E OA (open access)

Open access resource Economic profit: when revenues exceed costs (not accounting profit) Open access creates externality of entry. I’m making profit, that attracts you, you harvest fish, stock declines, profits decline. Entrants pay AC, get AR (not MC, MR) So fishers enter until AR = AC But, even open access is sustainable Though not socially desirable

Why manage fisheries? Otherwise, open access: externality of entry drives value of fishery to 0. May drive to extinction (or economic extinction) Non-extractive values ignored. Technology may destroy habitat, harvest individuals that should not be harvested, etc (another consequence of open access) Technology may improve, so management must keep up.

How manage fisheries? Depends largely on characteristics of fishery Biology & status of stocks History of extraction Commercial vs. subsistence, status of stocks Other values (non-extractive, recreational) May failures, some successes

Some management alternatives Harvest quotas (for whole fishery) Individual transferable quotas (ITQ, IFQ) Marine reserves (area closures) Season closures Ex-vessel tax (few) Regulated entry (licenses) Regulated efficiency (gear) Effort tax (few)

Small-scale fisheries Many small, multi-purpose boats Difficult to enforce regulations Local management most successful Kinship rights, social pressure Mainly limited entry, also gear, some area closures, etc. Often self-imposed. New entrants, technology, & markets are attractive; can be destructive

Baja California

History of cooperativas Pre-1991: “Reserved Species Regime” Lobster, abalone, etc. only harvested by fishing cooperatives (A property right) Post-1991: “Concession Regime” Gave access rights for 20 years in particular areas (benthic) or by boats (pelagic) (Another form of property right) Post-2000: “National Fishing Guide” Info on catch, status, management of 287 marine species (Pacific) – each fishery different.

Spiny Lobster Fishery

Maximum Sustainable Yield Maximum Sustainable Yield No increase in Fishing Effort No increase in Fishing Effort

Abalone Fishery

Overfished Overfished Quota system Quota system Reference point: Reference point: B t > B t-1 No increase in fishing effort

Pacific Ocean Fishing Areas - Cooperativas PNA BP PUR BT EMAN CSI LR PROG PA

Cooperativas Often devise own rules – social pressure to abide. Have exclusive rights to areas, self- enforce. Federal management supercedes - bargaining process with feds to determine management

Individual Transferable Quotas Regulator sets “total allowable catch” (TAC). Distributes quotas (auction, sell at fixed price, give away based on historical catch, or equal distribution) Quota rights can be traded. Some systems, buy right to harvest in perpetuity (as % of TAC)

ITQs and property rights Prior to 1976 coastal nations did not have rights to marine resources in “high seas” 1976 Magnuson Act & Law of the Sea: Grants rights to coastal nations to marine resources 200 miles from shore. But how to regulate within a country? ITQs effectively secure property rights to fish in the ocean. Lack of property rights is what causes problems with open access

Potential problems with ITQs Allocation of quotas? High-grading incentive Enforcement & administrative costs Most quotas held by largest firms “privatizing the oceans”? How set TAC in first place?

Alaskan Halibut Prior to adoption, season 1 day Poor fish quality, excessive investment for harvest, frozen most of year. Adopted 1995: free allocation to fishing vessels based on historic catch. Debit cards, fish tickets for enforcement A success, longer season, higher profits, more fish, bigger/better quality fish