Fleet dynamics of the SW Indian Ocean tuna Fishery : a bioeconomic approach Main results September 2013 C. Chaboud.

Slides:



Advertisements
Similar presentations
Basic Bioeconomics Model of Fishing
Advertisements

(Western) Channel Fisheries UK Finlay Scott, Trevor Hutton, Alyson Little, Aaron Hatcher cemare.
SOCIO ECONOMIC FACTORS AFFECTING EXPLOITATION AND MANAGEMENT OF TOP PREDATORS TOP PREDATORSP. M. Miyake.
Are the apparent rapid declines in top pelagic predators real? Mark Maunder, Shelton Harley, Mike Hinton, and others IATTC.
Sheng-Ping Wang 1,2, Mark Maunder 2, and Alexandre Aires-Da-Silva 2 1.National Taiwan Ocean University 2.Inter-American Tropical Tuna Commission.
1 1 Per Sandberg and Sigurd Tjelmeland Harvest rules and recovery strategies The case of Norwegian spring spawning herring.
The current status of fisheries stock assessment Mark Maunder Inter-American Tropical Tuna Commission (IATTC) Center for the Advancement of Population.
The economics of fishery management The role of economics in fishery regulation.
Barents Sea fish modelling in Uncover Daniel Howell Marine Research Institute of Bergen.
Are pelagic fisheries managed well? A stock assessment scientists perspective Mark Maunder and Shelton Harley Inter-American Tropical Tuna Commission
LECTURE. FORMATION OF PRICE FOR THE COMPANIES PRODUCT Plan lectures 1. Price and types of prices 2. Classification prices 3. Pricing policy of the enterprise.
Management issues, capacity building and research needs for capture fisheries By: Purwito Martosubroto National Commission for Fish Stock Assessment Ministry.
Renewable Common-Pool Resources: Fisheries and Other Commercially Valuable Species.
R. Sharma*, A. Langley ** M. Herrera*, J. Geehan*
The Maldives, a group of about 1,200 islands, separated into a series of coral atolls, is just north of the Equator in the Indian Ocean. Only 200 of the.
Copyright © 2009 Pearson Addison-Wesley. All rights reserved. Chapter 14 Renewable Common- Pool Resources: Fisheries and Other Commercially Valuable Species.
CMM Evaluation WCPFC6-2009/IP17 WCPFC6-2009/IP18 SPC Oceanic Fisheries Programme Noumea, New Caledonia.
Population Dynamics Mortality, Growth, and More. Fish Growth Growth of fish is indeterminate Affected by: –Food abundance –Weather –Competition –Other.
AGEC/FNR 406 LECTURE 27 Fisheries, Part II. Static-efficient sustained yield Gordon model (simplest approach) Goal: determine a catch level that provides.
Spatial issues in WCPO stock assessments (bigeye and yellowfin tuna) Simon Hoyle SPC.
Modeling growth for American lobster Homarus americanus Yong Chen, Jui-Han Chang School of Marine Sciences, University of Maine, Orono, ME
Fisheries in the Seas Fish life cycles: Egg/sperm pelagic larvaejuvenile (first non-feeding – critical period – then feeding) (first non-feeding – critical.
Framework for adaptation control information system in the Rio de la Plata: the case of coastal fisheries Walter Norbis – AIACC LA 32.
1 II-Main scientific and management results expected from the tagging programme 1) Stock structure and migrations 2) Tuna growth 3) Natural mortality as.
ALADYM (Age-Length Based Dynamic Model): a stochastic simulation tool to predict population dynamics and management scenarios using fishery-independent.
Economic impacts of changes in fish population dynamics: the role of the fishermen’s behavior Dipl.-Geogr. Peter Michael Link, BA Research Unit Sustainability.
2007 ICCAT SCRS Executive Summay for Atlantic Bigeye Tuna 2007 ICCAT SCRS Executive Summay for Atlantic Bigeye Tuna.
Data assimilation in APECOSM-E Sibylle Dueri, Olivier Maury
The management of small pelagics. Comprise the 1/3 of the total world landings Comprise more than 50% of the total Mediterranean landings, while Two species,
Fisheries 101: Modeling and assessments to achieve sustainability Training Module July 2013.
Renewable Common-Pool Resources: Fisheries and Other Commercially Valuable Species.
Fleet dynamics of the SW Indian Ocean tuna Fishery : a bioeconomic approach C. Chaboud UMR 212 EME IRD/IFREMER/UM2 )
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.
Oceans' Vocabulary Unit 4. GROUND FISH  fish that live on, in, or near the bottom of the body of water they inhabit.  Examples –cod, haddock, red fish,
O. Maury, MACROES meeting Brest 4-5 May 2010 MACROES WP 2 : Methodology in Ecosystems TASK 2.2: Improve the description of functional biodiversity within.
Yellowfin Tuna Major Changes Catch, effort, and length-frequency data for the surface fisheries have been updated to include new data for 2005.
PARTICIPANTS NCMR (Responsible Institute), IMBC [Greece] IREPA[Italy] U. Barcelona, U. Basque, UPO[Spain] EFIMAS MEETING NICOSIA CRETE 2004 APRIL
* Warm up * How overfishing affects productivity in marine food chains and food webs?
MONTE CARLO SIMULATION MODEL. Monte carlo simulation model Computer based technique length frequency samples are used for the model. In addition randomly.
Data requirement of stock assessment. Data used in stock assessments can be classified as fishery-dependent data or fishery-independent data. Fishery-dependent.
Day 4, Session 1 Abundance indices, CPUE, and CPUE standardisation
Stock Assessment Workshop 30 th June - 4 th July 2008 SPC Headquarters Noumea New Caledonia.
Closures. 2 Seasons –Can fish only at certain times. Areas –Fishing restricted in specific locations. Fisheries –Fishing is completely prohibited.
Species Interactions in the Baltic Sea -An age structured model approach PhD Student Thomas Talund Thøgersen.
Fish stock assessment Prof. Dr. Sahar Mehanna National Institute of Oceanography and Fisheries Fish population Dynamics Lab November,
Powerpoint Templates Page 1 EU-FIN PROJECT EUROPEAN UNION FISHING NETWORK The three main fishing activities exercised by Pegeia’s fishing fleet. Marios.
Summary of the Sevilla EFIMAS/COMMIT Economists meeting
Public Goods and Common Resources
FISHING EFFORT & CPUE.
Special Session: Landing Obligation
Pacific-Wide Assessment of Bigeye Tuna
Introduction to Economics of Water Resources Lecture 5
Indian Ocean: tropical tuna catches increasing rapidly over the last two decades Patudo Listao Albacore.
Growth rate (replacement) and size of the fish stock/pool
The role of scientific knowledge to inform investors in the Blue Economy The Seychelles tuna fisheries case study Francis Marsac, PhD Financing Sustainable.
Copyright © 2009 Pearson Addison-Wesley. All rights reserved.
Valuing the Linkages Between the Shrimp Fishery and Mangroves in Campeche, Mexico This case will provide an example of market based valuation.
TDW10: April 2016, Noumea, New Caledonia
ANALYSIS OF SKIPJACK CATCH PER UNIT OF EFFORT (CPUE) Mark N
Selectivity.
Evaluation of the 2004 Resolution on the Conservation of Tuna in the eastern Pacific Ocean (Resolution C-04-09)
Introduction The WCPO region comprises many different countries and territories, all of whom have direct or indirect fisheries based economic interests.
Steve Brouwer Oceanic Fisheries Programme Pacific Community
Country level implications
The use of Data in Fisheries Management
Copyright © 2009 Pearson Addison-Wesley. All rights reserved.
Evaluation of the 2004 Resolution on the Conservation of Tuna in the eastern Pacific Ocean (Resolution C-04-09)
Implications, adaptations & policies for economic development
Presentation transcript:

Fleet dynamics of the SW Indian Ocean tuna Fishery : a bioeconomic approach Main results September 2013 C. Chaboud

Main characteristics of model

Resources Three main tuna species : skipjack (SKJ), yellowfin tuna (YFT), big eye tuna (BET) and albacore (ALB) Migrating and straddling socks between EEZ’s and international waters Seasonal spatial repartition varying among species and age (differences between adults and juveniles) Most species are long living species

Fleets Fishing methods: purse seines (FADs + free schools), bait boats, longlines and gill nets. Differences in costs, in impacts on resource components by species or by age (catchability), in targeted markets and hence in prices Different countries or group of countries owning or exploiting tuna resources Fleets = sets of boats, defined by fishing methods and countries, and specific prices. Spatial fleet behavior (developed later)

Modeling choices Time step : month Simulation length : up to 25 years Age structured model (by month) Three species (SKJ, BET, YFT) Muti gears Three types of countries or owning and/or exploiting the resource Pure owners countries (don’t’ significantly exploited the resource Pure foreign fishing countries (no resource in the region) Owners and fishing countries

Modeling choices Spatially explicit model : resources and fleets are redistributed a each time step Different “layers” showing legal or technical constraints for access to resources Resources Fleets dynamics Position of harbors (fleets bases) exploitation results Distribution of exploitation results between fishing and resource owners countries. Model can be used in a reduced form (limited number of species, gears, fishing countries, cells…)

The grid 12 lines x 19 Columns 228 square cells 5° X 5 °

EEZs and legal boundaries layer Many cells are shared by different EEZs

Modeling choices Market : two possibilities Fishery is price taker(realistic for an isolated or limited exploitation system. Exogenous prices are defined by species, age (juveniles-adult) and fishing gear) Inverse demand function P = P(Q) (realistic if there is some coordination between all Tuna RFMOs for catch restriction or capacity control). Cost functions specified by fleet Fixed cost : insurance, depreciation, maintenance, fishing license fees… Variable costs : energy, food (linked to time at sea) labor (linked to yield value) royalties paied for access (linked to quantities …)

Resource Structured by age (age class = model time step = month) Catchability defined par species, gear and live stage (juvenile, adult) Von Bertalanffy growth curves, Natural mortality specified by age Different possibilities for recruitment Independent of dependent (hockey stick shaped) of fecund biomass Deterministic or stochastic (month and year effects)= Spatial monthly repartition per species and life stage (juvenile/adult) is due to 1. by a spatial preference matrix SP (different for adults and juveniles) and a spillover from each cell to adjacent cells. Sp can be modified during simulations to introduced changes in spatial preference 2. spillover : at each time step a constant part of each cell is redistributed to adjacent cells.

Spatial and temporal resource behavior At every time step resource N a (stock per species in number per age a ) less catch C a and natural mortality M a, is redistributed according to a spatial preference matrix SP aij, defined per month, species and life stage,. Cell ij time t Total stock Cell ij time t +1

Spatial and temporal resource behavior After the computation on the resource dynamics in number The biomass is obtained (for a species, a cell i,j and at age a) : The value of biomass is now computed, given an price vector by age (for a species) : Biomass values is used as input in the economic module of the model.

Spatial temporal Fleets behavior The total number of boats per fishing fleet (defined par a type of gear for a given country) can follow two types of time behavior Exogenous defined (fixed or varying during the simulation) Endogenous entry/exit behavior at the beginning of each year (ie every 12 time steps), depending from past year fleet cumulated profit (Smith model, 1968) :

Spatial temporal Fleets behavior : a free ideal distribution approach Two steps method : 1 )Fleets are first distributed among harbors, and 2 ) from harbors to cells Past characteristics (“value”) of cells are computed Biomass value of the cell in t-1 and t-12 Revenue per boat per cell in t-1 and t-12 Catch per boat per cell in t-1 and t-12. Profit per boat per cell in t-1 and t-12

Spatial temporal Fleets behavior : a free ideal distribution approach We compute first the « absolute value Of harbors (1) and then their « relative value » (2) which is their attractiveness h : harbor, b : fishing method, p : fishing country v = cell value dist= distance between harbor and cell Then each fleet is distributed between harbors (3)

Spatial temporal Fleets behavior : a free ideal distribution approach Then we compute the absolute (1) and relative (2) attractiveness for each cell cellule, for each fishing country (p), fishing method (b) and harbor (h) The boats can now be distributed between cells (3)

Spatial temporal Fleets behavior Particularity of the purse seine fishery : at each time step, the purse seine fleets are divided into two strategic components ‘Purse seines FAD’ and ‘Purse seines Free Schools’ according their relative economic results in t-1. The variation of the total number of purse seines of one fleet at the beginning of year y is obtained by adding their respective economic cumulated results (profit) over the past year.

Model outputs Biomass per species, cell, age, EEZ (in volume and value). Catches per species, age, fleet, fishing country, EEZ. Private profit per fleet. Current and discounted rent (NPV) per fishing and owners countries. Fleet number and spatial distribution Economic rent for states (private profit + net state incomes) current and discounted (NPV).

Control variables (defined before simulation) Initial fleet numbers (with possibility of effort multiplier varying during simulation) Fees and royalties MPA location (one or several adjacent or not grid cells) Control of access by resource owners (ie fishing agreements) Quotas, total or per ZEE (to be developped)