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Retrospective analyses, improvement of assessment and prediction methods

for haddock stocks.

A.A. Russkikh,

PINRO, Murmansk, Russia K.H. Hauge,

IMR, Bergen, Norway

Murmansk, 2005

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Contents

‡ Introduction

‡ Objectives of the work

‡ Statement of the problem

‡ Methods and results

‡ Conclusions

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Introduction

‡

NEA haddock annually asessed by AFWG using a catch at age model (VPA) that uses measurement of the number of fish caught in each age group

‡

In common with computing machinery evolution

the software for stock assessment and projection

was changed but calculations were made on the

same principle as previously

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Introduction

The standard software and methods used for stock assessment and projection of NEA haddock at AFWG*

Year

Assessment methods Short-term projection catch and biomass

Recruitment projection

1978 -1985 (Survey indices ratio)

1986-1991 IFAP module (VPA) RCRTINX2 (regressions

of yearclasses)

1992-1993

VPA version 3.1(SVPA/XSA),

ADAPT

1994-1998 VPA version 3.11 (SVPA/XSA) 1999-2002

IFAP module (management options

table)

2003-2005

VPA version 3.2 - VPA95 (SVPA/XSA)

MFDP(management options table)

RCT3 (regressions of yearclasses)

* - in brackets - methods

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Objectives of the work

‡

Current work will aim at investigating a part of the

uncertainty, i.e. observation errors given a particular model specification using ADAPT algorithm.

‡

Overall objective is to investigate if current assessment and projection procedures can be improved.

‡

It is expected that such improvements may provide for scientific advice. This will help solve main tasks of AFWG.

‡

Materials for investigation were input data for stock

assessment and projection which used in AFWG 2005

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Statement of the problem (Unsertainty)

‡ There are several categories of uncertainty in fish science:

¾ natural variation

¾ observation errors in input data

¾ model misspecification

¾ uncertainty in transaction scientific advices into management

¾ imperfect implementation of management strategies

¾ others

‰ Precautionary approach in fishery management which imply care fish stocks on a safe biological limits should (can) been based on total unsertainty estimates in stock assessment.

‰ The AFWG 2004 states that the uncertainty may be underestimated and that difference between Blim and Bpa may be too small therefore it should be investigated

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The current uncertainty is reflected in distance between lim and pa points which are adopted by ACFM for this stock as Blim=50 thou. t and Bpa =80 thou. t.

40 90 140 190 240 290

0.10 0.20 0.30 0.40 0.50 0.60

F 2004

SSB 2005

F lim F pa

B lim B pa

2004 AFWG estimates

reference points frame

2005 AFWG estimates

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Methods and results

40 90 140 190 240 290

0.1 0.2 0.3 0.4 0.5 0.6

F 2004

SSB 2005

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Methods and results

‡

Algorithm of adaptive framework ADAPT was

created in Excel and calculations done with input data from AFWG 2005.

‡

The purpose was estimate part of the assesment uncertainty, i.e. observation errors given a particular model specification, was characterized by using bootstrap methods.

‡

Bootstrap method based on principle random

resampling of the residuals from the observed-

predicted ”tuning” indices.

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Methods and results

Model calculated population parameters and recalculated a and b which correspond regressions, what provide smallest differences between observed” and “modeled” population abundance using used nonlinear least-squares minimization procedure

choused the “best” fit to the tuning indices.

0 2 4 6 8 10

1990 1995 2000 2005

Fleet 1 residuals

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Methods and results

‡The residuals of that fit were bootstrapped

0 2 4 6 8 10

1990 1995 2000 2005

Fleet 1 residuals

‡

1000 times and new values of N produced. The

distribution of the associated Fs and SSB provided

an indication of variation and the bias (deviations).

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Methods and results

SSB cumulativ e distribution

0.0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 1.0

0 100 200 300 400

Spawning stock biomass, thou.m.t.

Cumulative probability SSB 2003

SSB 2004 SSB 2005 SSB 2006 SSB 2007 Blim Bpa Spawning stock biomass

0 50 100 150 200 250 300

1980 1985 1990 1995 2000 2005

Biomass, thou. MT

80 % probability 95 % probability AFWG estimates

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Methods and results

F4-7 cumulative distribution

0.0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 1.0

0.1 0.2 0.3 0.4 0.5 0.6

Fishing mortality

Cumulative prbability

F4-7 2002 F4-7 2003 F4-7 2004 F4-7 2005 F4-7 2006 Flim Fpa Fishing mortality (age 4-7)

0.0 0.1 0.2 0.3 0.4 0.5 0.6 0.7

1980 1985 1990 1995 2000 2005

Fishing mortality

80% probability 95% probability AFWG estimates

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Methods and results

Recruitment (age 3)

0 200 400 600 800 1000 1200 1400 1600 1800 2000

1980 1985 1990 1995 2000 2005

Millions spec.

80% probability 95% probability AFWG estimates

N3 cumulative distribution

0.0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 1.0

0 200 400 600

millions spec.

Cumulative probability

N3 2003 N3 2004 N3 2005 N3 2006 N3 2007

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Conclusions

‡ Suggested algorithm based on ADAPT framework allow to investigate part of uncertainty in stock assessment and projection procedure and its prototype - program ADAPT can been applied as alternate approach for estimation of population dynamics of NEA haddock

‡ This uncertainty analysis is only the first step in the construction of full analysis of uncertainty in stock assessment.

‡ Additional work to more fully characterizes all important sources of uncertainty in the assessment process can been done by

working group members in relation to estimation more

conservative biological reference points and evaluation of the harvest control rules.

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Conclusions

‡ Main weakness of current methods for stock assessment and

projection is in using several partly different, partly similar models

‡ Models takes to account more or less the same input data but receives different estimation of population numbers and fishing mortality, therefore level of uncertainty increasing with each step.

‡ The framework should allow for a procedure stock assessment and short-term projection more simple, objective and robust to

criticism.

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Acknowledgments

‡ I would like to thank Kjellrun Hiis Hauge, IMR, Norway for her comments to the manuscript.

‡ I am also grateful to the Dr. Einar Hjorleifsson, MRI, Iceland who provides me strategy and practically helps, and gave me important advices for investigation of uncertainties in stock assessment.

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Спасибо за внимание!

Thanks for attention!

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