For 2014 Show the line of R producing SSB, and SSB producing R, and how they would spiderweb to get to equilibrium R. Took a long time, did not get to.

Slides:



Advertisements
Similar presentations
National Standard 1 Guidelines, Use of SPR reference points, and Incorporating uncertainty Grant Thompson Alaska Fisheries Science Center.
Advertisements

Issues in fisheries sustainability
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.
458 Delay-difference models Fish 458, Lecture 14.
Reliability and Limits of MSY Targets, Limits, and Uncertainty Rainer Froese GEOMAR, Kiel, Germany Public Hearing on Maximum Sustainable Yield European.
“Managing for Maximum Sustained Benefit” … is a challenging process that typically requires balancing competing and conflicting goals and interests, and.
458 Generation-Generation Models (Stock-Recruitment Models) Fish 458, Lecture 20.
Some basic tools for using population ecology as a management tool – A Primer GROWTH RECRUITMENT MORTALITY COMPENSATION.
458 Lumped population dynamics models Fish 458; Lecture 2.
Fishery Pacific Model Wakeland, Cangur, Rueda & Scholz International System Dynamics Conference (ISDC) Wayne Wakeland 1, Olgay Cangur 1, Guillermo.
Artificial Population Regulation n For regulation of populations n For commercial harvest n Maximum Sustained Yield (MSY) – Based on the logistic equation:
Barents Sea fish modelling in Uncover Daniel Howell Marine Research Institute of Bergen.
458 Policies and Their Evaluation Fish 458, Lecture 22.
458 Age-structured models Fish 458, Lecture Why age-structured models? Advantages: Populations have age-structure! More realistic - many basic.
Economics of Biotic Resources Ecosystem Structure and Function.
458 Fisheries Reference Points (Single- and multi-species) Fish 458, Lecture 23.
Biodiversity of Fishes Stock-Recruitment Relationships Rainer Froese,
458 Age-structured models (continued) Fish 458, Lecture 5.
1 Fisheries sustainability – CFP directions, MSFD descriptors and CSI Poul Degnbol Head of ICES advisory programme / ETC/W Marine and Coastal EEA/EIONET.
Recruitment success and variability in marine fish populations: Does age-truncation matter? Sarah Ann Siedlak 1, John Wiedenmann 2 1 University of Miami,
Fishery Management Fishing is extractive – Removes choices organisms- “ fine-ing ” – Changes food web structure The human condition provides little incentive.
Revisiting Stock-Recruitment Relationships Rainer Froese Mini-workshop on Fisheries: Ecology, Economics and Policy CAU, Kiel, Germany.
WP4: Models to predict & test recovery strategies Cefas: Laurence Kell & John Pinnegar Univ. Aberdeen: Tara Marshall & Bruce McAdam.
Population Dynamics Mortality, Growth, and More. Fish Growth Growth of fish is indeterminate Affected by: –Food abundance –Weather –Competition –Other.
Jo King: The Implications of Warming Climate for the Management of North Sea Demersal Fisheries R.M. Cook and M.R. Heath FRS Marine Laboratory, P.O. Box.
Fishery Biology. Fisheries Management n Provide people with a sustained, high, and ever-increasing benefit from their use of aquatic resources n Problems.
POPULATION DYNAMICS. POPULATION – POPULATION  DEF?? – POPULATION ECOLOGY CONCERNED WITH THE CHANGES IN POPULATION SIZE AND THE FACTORS THAT REGULATE.
Three Simple Rules for Ecosystem-Based Fisheries Management Rainer Froese GEOMAR, Kiel, Germany Presentation at the ICCAT workshop in Madrid, Spain, 9-11.
Surplus-Production Models
CPT Overfishing Working Group Crab Plan Team Presentation, September 2005.
A REVIEW OF BIOLOGICAL REFERENCE POINTS AND MANAGEMENT OF THE CHILEAN JACK MACKEREL Aquiles Sepúlveda Instituto de Investigación Pesquera, Av. Colón 2780,
Empirical and other stock assessment approaches FMSP Stock Assessment Tools Training Workshop Bangladesh 19 th - 25 th September 2005.
Oct. 6, Lecture 9 Population Ecology. Oct. 6, Today’s topics What is population ecology? Population change and regulation – Density independence.
Revisiting the SSC Decision to Use all Available Data to Calculate Average Landings/OFLs/ABCs Southeast Fisheries Science Center.
Lecture 2 review Compensatory rate change is the ecological basis for sustainable populations and harvesting Compensatory change may involve –Increases.
FTP Yield per recruit models. 2 Objectives Since maximizing effort does not maximize catch, the question is if there is an optimum fishing rate that would.
Harvesting and viability
MEDITERRANEAN SWORDFISH SCI-020. Background Unique genetic stock Some mixing with the N. Atlantic one Different biological characteristics than the Atlantic.
Stock Assessment Methodologies for Reef Systems: A Joint Analyses
Wildlife, Fisheries and Endangered Species
St. Thomas Grouper Analysis Carried out under STFA Funding Josh Nowlis, Ph.D. Stock Assessment Specialist.
Biodiversity of Fishes Stock-Recruitment Relationships
Why do we fish? Survival- many costal communities, particularly in developing countries, fish as a primary food source. Recreation- fishing for fun.
Atlantic bluefin tuna Two management units since 1981 Complex spatial dynamics with mixing between both stocks (investigated by BFT-SG since 2001) Spatial.
1 Climate Change and Implications for Management of North Sea Cod (Gadus morhua) L.T. Kell, G.M. Pilling and C.M. O’Brien CEFAS, Lowestoft.
A Common Sense Approach to Ecosystem- Based Fisheries Management In this study we show that substantial gains towards the goals of ecosystem-based fisheries.
Yellowfin Tuna Major Changes Catch, effort, and length-frequency data for the surface fisheries have been updated to include new data for 2005.
Lecture 10 review Spatial sampling design –Systematic sampling is generally better than random sampling if the sampling universe has large-scale structure.
Quiz 7. Harvesting strategies and tactics References Hilborn R, Stewart IJ, Branch TA & Jensen OP (2012) Defining trade-offs among conservation, profitability,
Continuous logistic model Source: Mangel M (2006) The theoretical ecologist's toolbox, Cambridge University Press, Cambridge This equation is quite different.
Data requirement of stock assessment. Data used in stock assessments can be classified as fishery-dependent data or fishery-independent data. Fishery-dependent.
Population Growth CENV 110. Topics Basic Population Dynamics Human Population Dynamics Sustainable Harvesting of Wild Populations.
C5 - Population Ecology. Read & Consider C.5.1 What techniques do we already know for estimating population?
Delay-difference models. Readings Ecological Detective, p. 244–246 Hilborn and Walters Chapter 9.
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.
Age-structured models. Background readings Lawson TA & Hilborn R (1985) Equilibrium yields and yield isopleths from a general age-structured model of.
IBFMPs Goals and Objectives
Management Regulations
Age-structured models Yield-per-recruit, reference points, MSY
Maximum Sustainable Yield & Maximum Economic Yield
Lecture 12: Population dynamics
MSY from age-structured models
MSFD Descriptor 3 population age and size distribution indicative of a healthy stock Gerjan Piet & Thomas Brunel.
Day 2 Session 2 Biological reference points - Supplementary
CHANGES to ECOSYSTEMS and POPULATIONS
Models used for stock recruits and parent stock
Beverton and Holt’s yield per Recruit Model
BIOMASS PER RECRUIT MODEL
YIELD CURVES.
Fisheries Models To produce a good fisheries model, we must account for all contributions to reproduction, growth, and mortality, throughout the life cycle.
Presentation transcript:

For 2014 Show the line of R producing SSB, and SSB producing R, and how they would spiderweb to get to equilibrium R. Took a long time, did not get to the end stuff after Sustainable Fisheries Act.

Age-structured models part 2

Today Yield-per-recruit analysis: SBPR, YPR Reference points: B 40%, F max, R 0, SSB 0, MSY, B MSY, u MSY How to use the Table Function in Excel (Data->What If Analysis->Data Table) Discrete vs. continuous fishing

Review: Basic age-structured model sexes grouped The “plus” group Egg production Recruitment Catch weight a function of egg production e.g. Beverton-Holt Ages between 1 and n Mass at age Natural survival rate (0-1) Exploitation rate (0-1) Vulnerability (0-1) All individuals identical above the plus group age Fecundity

Review: starting conditions (t = 1) Starting recruitment Natural survival rate Exploitation rate Vulnerability Numbers in plus group age n

Yield-per-recruit analysis Tracking one recruit (or one cohort) At different exploitation rates (u t ), what is the lifetime expected spawning biomass (egg production) of one recruit? What is the lifetime expected yield (catch) from one recruit? What exploitation rate would maximize yield? What is MSY (maximum sustainable yield)?

SBPR and YPR One recruit (one individual) Natural survival rate Exploitation rate Vulnerability Plus group age Fecundity Weight-at-age Spreadsheet: “4 per recruit analysis.xlsx”

YPR is different from full age- structured model One recruit (not R 0 ) Only analyzing one cohort, not impacts on multiple generations No recruitment function

4 per recruit analysis.xlsx, sheet YPR and SBPR

Typical calculations YPR and SBPR as function of exploitation rate u What is the impact of changing vulnerability through regulations? Many reference points used in fisheries

YPR and SBPR as a function of exploitation rate u Spreadsheet: “4 per recruit analysis.xlsx”

Key issues in yield-per-recruit The two most common YPR shapes are (1) asymptotic and (2) a curve that peaks and then gradual declines Vulnerability to fishing determines which pattern occurs: when vulnerability occurs before growth has slowed, then YPR may rise and then decline

Reference points based on YPR and SBPR Egg production: F 40% is the fishing mortality rate at which SBPR is 40% of maximum (also F 35%, F 50%, etc.) F max is the fishing mortality rate that maximizes YPR, where this exists For many species where there is little concern about recruitment overfishing, yield-per-recruit dominates (since it is assumes there is no change in recruitment)

F max and F 40% From yield-per-recruit, no stock-recruit relationship 4 per recruit analysis.xlsx, sheet YPR by u F 40% SBPR 0 0.4×SBPR 0 F max

F max can be undefined Each curve has a different age for when fish are vulnerable to fishing, at 5 yr there is no defined F max 1 yr 2 yr 3 yr 4 yr 5 yr = F max 4 per recruit analysis.xlsx, sheet Fmax

Unfished spawning biomass In the absence of harvest, spawning biomass per recruit SBPR 0 is the same as the total egg production in the yield-per- recruit calculations Therefore unfished spawning biomass (common symbols are SSB 0, B 0, SB 0 or E 0 ) is SBPR 0 multiplied by recruitment in the unfished population (R 0 )

Equilibrium recruitment for exploitation rate u Beverton-Holt equation, recruits depend on spawners Spawners depend on recruits

Calculating MSY and B MSY Unlike YPR calculations of F max, this needs the stock-recruit relation At a given harvest rate, total yield = yield- per-recruit × recruitment, or C = YPR × R Given this model we can calculate MSY and B MSY by using analytic formulae for the yield as a function of exploitation rate. MSY is the highest yield, B MSY is the stock size that produces the highest yield

loop over different values of u calculate SBPR(u), YPR(u) calculate R(u), C(u), SSB(u) end loop over values of u MSY is maximum C(u) SSB MSY is the spawning stock biomass at the u that produces MSY u MSY is the exploitation rate u producing MSY

4 MSY Bmsy.xlsx sheet “MSY Bmsy”

Equilibrium exploitation vs. catch u MSY MSY Unsustainable (u)(u) 4 MSY Bmsy.xlsx sheet “MSY Bmsy”

Spawning output vs. catch SSB MSY MSY 4 MSY Bmsy.xlsx sheet “MSY Bmsy” SSB MSY at 26% of SSB 0 SSB 0

Total biomass vs. catch B MSY (or TB MSY ) MSY 4 MSY Bmsy.xlsx sheet “MSY Bmsy” B0B0 TB MSY at 32% of TB 0

Reference point: B MSY B MSY —biomass that produces maximum sustained yield—used to be a target for fisheries management, but now often treated as a lower limit MSY—also known as the optimum yield

Sustainable Fisheries Act 2007 (16 U.S.C , updated from 1977 Magnuson-Stevens Act) (33) The term “optimum”, with respect to the yield from a fishery, means the amount of fish which— (A) will provide the greatest overall benefit to the Nation, particularly with respect to food production and recreational opportunities, and taking into account the protection of marine ecosystems; (B) is prescribed as such on the basis of the maximum sustainable yield from the fishery, as modified reduced by any relevant economic, social, or ecological factor; and (C) in the case of an overfished fishery, provides for rebuilding to a level consistent with producing the maximum sustainable yield in such fishery. i.e. B MSY Changed in 1996

MSY most affected by steepness and natural mortality Natural survival = 0.9Natural survival = 0.5 Exploitation rate (u) 4 MSY Bmsy.xlsx sheet “MSY by h and s”

Key characteristics of “basic” age-structured models Time-invariant production relationship All models totally stable, if you stop fishing at any level the population recovers All models show higher rates of increase at lower densities

What age-structured models can’t do Very little: almost any desired feature can be added to the basic framework (e.g. depensation, density-dependent growth and survival, environmental effects on recruitment and survival) Can think of these models as a general framework in which to embed specific recruitment, growth and survival hypotheses

Common extensions Splitting the sexes: especially when growth and vulnerability differ by sex Explicit partitioning between mature and immature, or vulnerable and not vulnerable individuals Splitting by space

What to know What are the terms B 40%, F max, R 0, SSB 0, MSY, B MSY, u MSY What determines shape of yield-per-recruit What determines shape of total yield curve (exploitation rate vs. yield) How to derive equilibrium recruitment How to estimate MSY, B MSY