An initial investigation of the information content of sole catch-atlength distributions regarding recruitment trends

Similar documents
Assessment of the South African anchovy resource using data from : posterior distributions for the two base case hypotheses

An Alternative SSASPM Stock Assessment of Gulf of Mexico Vermilion Snapper that Incorporates the Recent Decline in Shrimp Effort.

J.P. Glazer and D.S. Butterworth

Trends in policing effort and the number of confiscations for West Coast rock lobster

UPDATED 2016 GLMM -STANDARDISED LOBSTER CPUE FROM THE TRISTAN DA CUNHA OUTER GROUP OF ISLANDS. S.J. Johnston, A. Brandão and D.S. Butterworth.

Final Anchovy and Sardine TACs and TABs for 2016, Using OMP-14

Each cruise consists of a series of individual trawls conducted at different stations. The sampling procedure followed for each trawl is as follows:

Influence of feeding conditions on breeding of African penguins importance of adequate local food supplies

Fisheries, Population Dynamics, And Modelling p. 1 The Formulation Of Fish Population Dynamics p. 1 Equilibrium vs. Non-Equilibrium p.

Delta-lognormal linear models applied to standardised CPUE abundance indices (1994 to 2003) for orange roughy off Namibia.

Final Anchovy TAC and Sardine TAB for 2011, Using OMP-08

New Zealand Fisheries Assessment Report 2017/26. June J. Roberts A. Dunn. ISSN (online) ISBN (online)

Trevor Davies, Dalhousie University, Halifax, Canada Steven J.D. Martell, International Pacific Halibut Commission, Seattle WA.

Spatially explicit population dynamics models for

Dab (Limanda limanda) in Subarea 4 and Division 3.a (North Sea, Skagerrak and Kattegat)

Spanish Mackerel and Cobia Abundance Indices from SEAMAP Groundfish Surveys in the Northern Gulf of Mexico. AG Pollack and GW Ingram, Jr SEDAR28 DW03

A State-Space Model for Abundance Estimation from Bottom Trawl Data with Applications to Norwegian Winter Survey

Automated Likelihood Based Inference for Stochastic Volatility Models using AD Model Builder. Oxford, November 24th 2008 Hans J.

Supplementary Material for:

2) MFMR Ministry of Fisheries and Marine Resources, PO Box 912, Swakopmund, Namibia.

JIMAR PFRP ANNUAL REPORT FOR FY 2007

Synthesis and Integrated Modeling of Long-term Data Sets to Support Fisheries and Hypoxia Management in the Northern Gulf of Mexico

Assessing the impacts of endocrine disrupting compounds (EDCs) on fish population dynamics: a case study of smallmouth bass in Chesapeake Bay

Falkland Island Fisheries Department. Golden Chicha (ZDLC1) Falkland Islands. Ignacio Payá. - March

Adjoint-based parameter estimation for the spatially explicit model of large pelagics (with application to skipjack tuna).

Chapter 1 Statistical Inference

Reported commercial landings of red drum in Florida and estimated annual length and age composition.

Falkland Island Fisheries Department. Loligo gahi Stock Assessment Survey, First Season Argos Vigo (ZDLU1) Falkland Islands

Potential of Observer Data for Assessment: Standardizing CPUE from the Eastern Aleutian Islands Golden King Crab Fishery Observer Data

SEDAR 42- DW November 2014

Annex 7. Jack mackerel stock assessment

SUPPLEMENTARY INFORMATION

Annex 8. Jack mackerel stock assessment

Using GLM and VAST to Estimate CPUE Indices from Fishery Dependent Data: Aleutian Islands Golden King Crab

Progress report on development of a spatially explicit operating model for tropical tuna populations.

Post-Graduation Plans stock assessment scientist (NOAA, hopefully)

DESCRIPTION AND ANALYSIS OF THE GAMBIA SOLE STOCK ASSESSMENT 2012

RATING TRANSITIONS AND DEFAULT RATES

MULTIFAN-CL: a length-based, age-structured model for fisheries stock assessment, with application to South Pacific albacore, Thunnus alalunga

UPDATED STANDARDIZED CATCH RATES FOR BLUEFIN TUNA (Thunnus thynnus) FROM THE TRAP FISHERY IN THE STRAITS OF GIBRALTAR

Maryland Oyster Stock Assessment Update. December 18, 2017 St. Mary s City, MD

Statistical Data Analysis Stat 3: p-values, parameter estimation

2/23/2015 GEOGRAPHY 204: STATISTICAL PROBLEM SOLVING IN GEOGRAPHY THE NORMAL DISTRIBUTION THE NORMAL DISTRIBUTION

AN APPLICATION OF AN INTEGRATED STOCK ASSESSMENT MODEL (STOCK SYNTHESIS) TO EASTERN ATLANTIC BLUEFIN TUNA STOCK

Environmental changes

JIMAR PFRP ANNUAL REPORT FOR FY 2005

Statistics 572 Semester Review

SCIENTIFIC COMMITTEE ELEVENTH REGULAR SESSION Pohnpei, Federated States of Micronesia 5 13 August 2015

STAT 201 Assignment 6

The observed global warming of the lower atmosphere

Data files and analysis Lungfish.xls Ch9.xls

UPDATED JAPANESE LONGLINE BLUEFIN TUNA CPUE IN THE ATLANTIC OCEAN

Modelling cannibalism and inter-species predation for the Cape hake species Merluccius capensis and M. paradoxus

Gravity Models, PPML Estimation and the Bias of the Robust Standard Errors

7. Integrated Processes

Inference with Simple Regression

AP-Optimum Designs for Minimizing the Average Variance and Probability-Based Optimality

Current and future climate of the Cook Islands. Pacific-Australia Climate Change Science and Adaptation Planning Program

Characteristics of Fish Populations. Unexploited Populations. Exploited Populations. Recruitment - Birth Mortality (natural) Growth

Appendix 1: UK climate projections

Estimating the distribution of demersal fishing effort from VMS data using hidden Markov models

7. Integrated Processes

Analyzing population dynamics of Indian Ocean albacore (Thunnus alalunga) using Bayesian state-space production model

USP. Estimating mortality

Applied linear statistical models: An overview

SCW6-Doc05. CPUE standardization for the offshore fleet fishing for Jack mackerel in the SPRFMO area

Length-weight relationships and condition factors of Red sole, Cynoglossus senegalensis and Black sole, Synaptura cadenati from The Gambia

EVA Tutorial #2 PEAKS OVER THRESHOLD APPROACH. Rick Katz

SUPPLEMENTARY INFORMATION

Current and future climate of Vanuatu. Pacific-Australia Climate Change Science and Adaptation Planning Program

Outline lecture 2 2(30)

Graphing and Writing Linear Equations Review 3.1, 3.3, & 4.4. Name: Date: Period:

UNIVERSITY OF MASSACHUSETTS Department of Mathematics and Statistics Basic Exam - Applied Statistics January, 2018

Introduction to Statistical Analysis using IBM SPSS Statistics (v24)

Spatio-temporal models for populations

Draft AFS Spatial Processes

A state-space multi-stage lifecycle model to evaluate population impacts. in the presence of density dependence: illustrated with application to

Stat 587: Key points and formulae Week 15

Modeling the atmosphere of Jupiter

Science, Post Office Box 38, Solomons, Maryland, 20688, USA. Version of record first published: 10 Sep 2012.

Towards spatial life cycle modelling of eastern Channel sole

Marine Heat Waves: A general overview and case studies in the Mediterranean and around Australia. Eric C. J. Oliver1,2

Population Dynamics of Gulf Blue Crabs. Caz Taylor & Erin Grey Department of Ecology & Evolutionary Biology Tulane University

UNIVERSITY OF CAMBRIDGE INTERNATIONAL EXAMINATIONS General Certificate of Education Advanced Level

Fusing point and areal level space-time data. data with application to wet deposition

Ph.D. Qualifying Exam Friday Saturday, January 3 4, 2014

Use of Ocean Observations to Develop Forecasts in Support of Fisheries Management

DESCRIPTION AND ANALYSIS OF THE GAMBIA SOLE STOCK ASSESSMENT 2013

Oikos. Appendix A1. o20830

Blueline Tilefish Assessment Approach: Stock structure, data structure, and modeling approach

An Application of Perturbation Methods in Evolutionary Ecology

Bayesian state-space production models for the Indian Ocean bigeye tuna (Thunnus Obesus) and their predictive evaluation

SUPPLEMENTAL MATERIALS FOR:

Chapter 5. Bayesian Statistics

Lansing, Michigan, 48824, USA e Georgia Cooperative Fish and Wildlife Research Unit, Warnell School of Forestry and

Assessment of environmental correlates with the distribution of fish stocks using a spatially explicit model

Relationship between temperature and fluctuations in sandfish catch (Arctoscopus japonicus) in the coastal waters off Akita Prefecture

Motion Graphs Practice

TOTAL EQUILIBRIUM YIELD

Validation and comparison of numerical wind atlas methods: the South African example

Transcription:

An initial investigation of the information content of sole catch-atlength distributions regarding recruitment trends A. Ross-Gillespie and D.S. Butterworth 1 email: mlland028@myuct.ac.za Summary A simple analysis of sole catch-at-length distributional data is carried out to estimate recruitment trends, assuming that availability and mortality do not change over time. Although the information content of these data is limited, they do provide give some indication of a period of generally below average recruitments during the first decade of the century, suggesting justification for expanding to a statistical-catch-at-length (SCAL) assessment in due course. Introduction At present sole assessments are based on production models which aggregate over the length composition information available for the fishery and use only catches and the annual CPUE values for input. Such assessments could be extended to a full Statistical-Catch-at-Length (SCAL) approach, but this would require a fair amount of person-power resources to implement. Before doing so therefore, this initial and relatively simple analysis has been implemented to attempt to coarsely ascertain the information content of the sole CAL data in an assessment context. The key feature of this simple approach is to assume that the primary driver of the dynamics is recruitment variability, so that it is attempting to estimate the trend in recruitment strength over time under the assumptions that quantities such as fishing mortality show much less variation over time. Data Commercial catch-at-length data are available for the years 1995 to 2015. A growth curve is taken from Payne et al. (1986) for the area west of 24 E: L = 54.739, κ = 0.176, t 0 = 0.089 Methods The population dynamics are given by: N y+1,a+1 = g an y,a (1) where N y,a g a is the number of fish in age group a at the start of year y available to the fishery, and is a function that combines the effects of mortality (both natural and fishing) and availability of age-group a to the fishery, given by: g est a for a min a 4 g a = 1 for a=5 g 5e α(a 5) for 5 < a a max 1 (2) 1 Marine Resource Assessment and Management Group, University of Cape Town, Rondebosch, 7701 1

where a min and a max are the minimum and maximum ages considered in the model, and g est a parameters. Table 1 lists the values assumed for these ages. and α are estimable For each year, the number of fish available to the fishery in the lowest age-group (expressed in relative rather than absolute quantities) is given by: N y,amin = e ɛy (3) where ɛ y are estimable parameters, i.e. recruitment to the fishery is modelled as fluctuations about a flat trend. If y 0 is the first year in the assessment (i.e. 1995), then N y0 1,a min is treated as an additional estimable parameter. Furthermore equilibrium is assumed in year y 0 1 so that N y0 1,a+1 = g an y0 1,a, thus allowing an initial population structure to be calculated. The model-predicted catch-proportions-at-age are calculated as: p y,a = N y,a a N y,a The model-predicted catch-proportions-at-length are derived from the catches-at-age by: (4) p y,l = a p y,aa a,l (5) where A a,l is the proportion of fish of age a to be found in the length group l. This matrix is calculated assuming that for each age a, the lengths are normally distributed about a mean given by the growth curve, i.e. L a N ( [L ) ] 1 e κ(a t 0) ; θa 2 (6) The variance θ 2 a is given by: θ a = φl a (7) where l a is the expected length at age a, and φ is fixed at 0.05 for the results shown in this document. If p obs y,l are the proportions-at-length calculated from the observed catch-at-length data, then under the assumption of (possibly overdispersed) multinomial error distributions, which can be rendered approximately homoscedastic normal through a square root transformation, the likelihood contribution is given by: lnl = [ lnσ p + 1 ( p obs 2σ 2 y,l ) 2 ] p y,l y p l where the variance parameter σ p is taken to be its maximum likelihood estimate from Equation 8: 1 ( σ p = y l 1 p obs y,l ) 2 p y,l (9) y Furthermore, a penalty is added to the negative log-likelihood to stabilise estimation of the strength of cohorts towards the start and end of the time series which have not been sampled on many occasions; this is done by effectively assuming a prior of a normal distribution for each ɛ y: where σ ɛ = 0.2 for the results in this document. pen = y l (8) ɛ 2 y/(2σ 2 ɛ ) (10) The analysis was performed in AD Model Builder (Fournier et al. 2012). 2

Results and Discussion Table 2 lists the estimates and the standard errors for the recruitment residuals. Figure 1 shows the fits to the catch-atlength data. This Figure also shows the model-predicted proportions-at-age. Figure 2 shows selected summary outputs from the model, as detailed in the Figure caption. This analysis was intended as exploratory only in nature, so that sensitivities (e.g. to the values of φ and σ ɛ) have not yet been investigated. The catch-at-length data clearly contain limited information, as indicated by the small extent of variation over the years in the mean of these length distributions (see Figure 2(B)), though those means do nevertheless indicate some slight general reduction over time. However the most important output is the relative recruitment estimates shown in Figure 2(E). These do seem to give some indication of a period of generally below average recruitments during the first decade of the century, which possibly links to the drop experienced in CPUE over that period. This signal in these length data would seem to indicate sufficient information content in those data to justify expanding to a SCAL assessment in due course. References Payne, A.I.L. 1986. Biology, stock integrity and trends in the commercial fishery for demersal fish on the south-east coast of South Africa. PhD Thesis, University of Port Elizabeth. v+368 pp. Fournier, D. A., Skaug, H. J., Ancheta, J., Ianelli, J., Magnusson, A., Maunder, M. N., Nielsen, A. and Sibert, J. 2012. AD Model Builder: using automatic differentiation for statistical inference of highly parameterized complex nonlinear models. Optimization Methods and Software, 27(2), 233249. 3

Table 1: List of the model parameters and their descriptions. Parameter Description a min a max l min Minimum age considered in the model, 4 years; this was chosen as the growth curve and catch-at-length distributions suggest minimal catch of sole of ages less than 4. Maximum age considered in the model, 9 years; the combination of growth curve and catchat-length distributions suggest few sole caught of greater ages than this. Length minus-group; quantities and data below 25cm are pooled into this minus group so that no length group contains less than 2% of the total observations (summed across the years). l max Length plus-group; quantities and data above 42cm are pooled into this plus group. Note that the 40 and 41cm groups have additionally been pooled into a single group, so that this combined group meets the 2% threshold. g 4, g 5, α Estimable parameters for the g function (Equation 2). φ The variance parameter for the growth-curve, fixed at 0.05 (Equation 7). Table 2: Estimates and standard deviations for ɛ y (Equation 3). Year Estimate Standard error 1994-0.090 0.169 1995-0.365 0.150 1996-0.094 0.147 1997 0.306 0.131 1998 0.284 0.135 1999 0.292 0.133 2000 0.025 0.135 2001-0.096 0.134 2002-0.007 0.134 2003-0.092 0.143 2004-0.280 0.145 2005-0.298 0.145 2006-0.243 0.133 2007 0.100 0.131 2008 0.254 0.130 2009-0.046 0.135 2010-0.236 0.135 2011-0.180 0.133 2012 0.015 0.134 2013 0.201 0.138 2014 0.577 0.149 2015-0.027 0.176 4

5 Catch at size proportions 1995 2000 2004 2009 2013 1997 2001 2006 Age (years) 2010 2014 Length (cm) 1998 2002 2007 2011 2015 1999 2003 2008 2012 Observed catches Model proportions at length Model proprotions at age Figure 1: Fit to catch-at-length proportions. The grey shaded area shows the observed catch-at-length proportions, while the solid black lines show the modelpredicted proportions-at-length (Equation 5). The lower (black) horizontal axis represents length in cm, while the upper (blue) horizontal axis represents age, where each age is located at the expected length from the growth curve equation. The dashed blue lines show the model-estimated proportions-at-age. Note that the observed and model-predicted proportions-at-length have been pooled below the length of 25cm (the minus group) and above the length of 42cm (the plus group), so that no length class has less than 2% of the total number of observations. Furthermore, observations from length groups 40 and 41cm have been combined into a single group to also meet this 2% threshold.

6 1995 1997 1998 1999 2000 2001 2002 2003 2004 2006 2007 2008 2009 2010 2011 2012 2013 2014 2015 (A) Observed catch proportions at length mean: 32.45 sd: 3.61 mean: 31.14 sd: 3.58 mean: 31.42 sd: 3.40 mean: 32.57 sd: 3.71 mean: 33.01 sd: 3.22 mean: 33.49 sd: 2.99 mean: 32.78 sd: 3.23 mean: 32.90 sd: 3.33 mean: 32.87 sd: 3.31 mean: 32.29 sd: 3.88 mean: 31.36 sd: 4.72 mean: 31.22 sd: 3.58 mean: 31.92 sd: 3.64 mean: 33.22 sd: 3.72 mean: 32.42 sd: 3.90 mean: 31.07 sd: 4.15 mean: 31.20 sd: 4.25 mean: 31.63 sd: 3.79 mean: 31.93 sd: 3.24 20 45 50 55 Length (cm) Length g(a) 0.0 0.5 1.0 1.5 2.0 (B) Yearly means of the observed catches at length 1995 2000 2005 2010 2015 Year (D) g vector as a function of age Age Length 0 10 20 30 40 50 Recruitment 0.0 0.5 1.0 1.5 2.0 phi = 0.05 (C) Age length distributions 10 Age (E) Relative recruitment at age 4 (exp(ε y )) 1995 2000 2005 2010 2015 Year Figure 2: Selected model outputs. Panel (A) shows the (unpooled) observed catch-at-length proportions from Figure 1, and also shows the mean and standard deviation of the distribution for each year in the top right legend. Panel (B) then plots these means against time and shows the 95% probability intervals given by twice the standard deviation. Panel (C) shows the length distribution assumed in the model for each age group. The greyed-out area indicates the lengths that fall into the plus and minus groups. Panel (D) shows the estimated g vector from Equation 2. Panel (E) shows the estimated recruitment values, given by the exponential of the residuals (Equation 3), along with their 95% confidence intervals given by twice the exponential of the standard errors estimated for ɛ y (the ɛ y estimates and standard errors are given in Table 2).