CPUE analysis methods, progress and plans for 2011 Simon Hoyle.

Slides:



Advertisements
Similar presentations
Are the apparent rapid declines in top pelagic predators real? Mark Maunder, Shelton Harley, Mike Hinton, and others IATTC.
Advertisements

Peter Ward RAM Myers Dalhousie University The effects of soak time and depth on longline catch rates EB WP-3 EB WP-12.
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.
Dealing with interactions between area and year Mark Maunder IATTC.
The current status of fisheries stock assessment Mark Maunder Inter-American Tropical Tuna Commission (IATTC) Center for the Advancement of Population.
Are pelagic fisheries managed well? A stock assessment scientists perspective Mark Maunder and Shelton Harley Inter-American Tropical Tuna Commission
Mark N. Maunder, John R. Sibert, Alain Fonteneau, John Hampton, Pierre Kleiber, and Shelton J. Harley Problems with interpreting catch-per-unit-of-effort.
Effect of Circle Hooks and Bait on Target and Bycatch Species in Pelagic Longline Fisheries 2007 Inter-Sessional Meeting of the Subcommittee on Ecosystems.
The length structure of bigeye tuna and yellowfin tuna catch at different depth layers and temperature ranges: an application to the longline fisheries.
R. Sharma*, A. Langley ** M. Herrera*, J. Geehan*
Standardizing catch per unit effort data
CMM Evaluation WCPFC6-2009/IP17 WCPFC6-2009/IP18 SPC Oceanic Fisheries Programme Noumea, New Caledonia.
ASSESSMENT OF BIGEYE TUNA (THUNNUS OBESUS) IN THE EASTERN PACIFIC OCEAN January 1975 – December 2006.
Facts & hypothesis upon Indian Ocean billfishes, by Alain Fonteneau SWO is a deep species (at least during the day), when all other BILL are shallow species:
Where does my data go? Preparation of files for the assessments of IOTC stocks and use of data for the assessments of IOTC species Mauritius, March.
REPORT OF THE 2007 MEETING OF THE SUB- COMMITTEE ON ECOSYSTEMS (Madrid, Spain - February 19 to 23, 2007)
Stock assessment of yellowfin tuna in the Indian Ocean using MULTIFAN-CL (IOTC-2011-WPTT13-36). Adam Langley, Miguel Herrera and Julien Million.
Spatial issues in WCPO stock assessments (bigeye and yellowfin tuna) Simon Hoyle SPC.
Report of Chinese Observer Program in the Tropical Eastern Pacific Ocean in 2006 Xiao-jie Dai, Liu-xiong Xu and Li-ming Song Shanghai Fisheries University,
STANDARDIZATION OF CPUE FROM ALEUTIAN ISLANDS GOLDEN KING CRAB FISHERY OBSERVER DATA M.S.M. Siddeek 1, J. Zheng 1, Doug Pengilly 2, and Gretchen Bishop.
Historical and recent estimates of the body-size and abundance of pelagic species taken by longline Peter Ward RAM Myers Dalhousie University EB WP-7.
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.
Summary of Atlantic Swordfish Species Working Group Discussion (see also SCI -021)
Objective Data  The outlined square marks the area of the study arranged in most cases in a coarse 24X24 grid.  Data from the NASA Langley Research Center.
2007 ICCAT SCRS Executive Summay for Atlantic Bigeye Tuna 2007 ICCAT SCRS Executive Summay for Atlantic Bigeye Tuna.
METHODS WORKING GROUP March 19 to 23, 2007 SCI-028 EXECUTIVE SUMMARY SCI-032 DETAILED REPORT.
CATCH LIMITS FOR INDIVIDUAL PURSE-SEINE VESSELS TO REDUCE FISHING MORTALITY ON BIGEYE TUNA IN THE EASTERN PACIFIC OCEAN.
USING INDICATORS OF STOCK STATUS WHEN TRADITIONAL REFERENCE POINTS ARE NOT AVAILABLE: EVALUATION AND APPLICATION TO SKIPJACK TUNA IN THE EASTERN PACIFIC.
Incorporating spatial autocorrelation into the general linear model with an application to the yellowfin tuna (Thunnus albacares) longline CPUE data 將空間自我相關與泛線性模式結合,並應.
Predicting yellowfin tuna recruitment in EPO using on oceanographic data. Adam Langley OFP, SPC.
The effect of variable sampling efficiency on reliability of the observation error as a measure of uncertainty in abundance indices from scientific surveys.
Is there a ‘cryptic biomass’ of relatively old and large red snapper in southeast US continental shelf-break waters?
Scallop Dive (Port Phillip Bay) Fishery Cover photo - PMSS COMMERCIAL SCALLOP DIVE FISHERY - PORT PHILLIP BAY Results of the Fishery-Independent Dive Survey.
ASSESSMENT OF BIGEYE TUNA (THUNNUS OBESUS) IN THE EASTERN PACIFIC OCEAN January 1975 – December 2005.
Management of the brown crab (Cancer pagurus) fishery in Ireland Oliver Tully Irish sea Fisheries Board (BIM)
A general covariate based approach for modeling the population dynamics of protected species: application to black footed albatross (Phoebastria nigripes)
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.
Modelling population dynamics given age-based and seasonal movement in south Pacific albacore Simon Hoyle Secretariat of the Pacific Community.
Influence of selectivity and size composition misfit on the scaling of population estimates and possible solutions: an example with north Pacific albacore.
1 PIRO’s Pelagic Ecosystem Management Needs PIFSC External Science Review April 5, 2016.
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.
Population Dynamics and Stock Assessment of Red King Crab in Bristol Bay, Alaska Jie Zheng Alaska Department of Fish and Game Juneau, Alaska, USA.
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.
Albacore CPUE based on joint analysis Simon Hoyle, Yin Chang, Doo Nam Kim, Sung Il Lee, Takayuki Matsumoto, Kaisuke Satoh, and Yu-Min Yeh.
Pacific-Wide Assessment of Bigeye Tuna
Estimation of Catches of Non-Target Species Using Observer Data
Indian Ocean: tropical tuna catches increasing rapidly over the last two decades Patudo Listao Albacore.
Day 1 Sessions 1-3 Revision
Mix of species KEPT on 1512 observed Trawl trips, consisting of 20,420 tows, 2005
TDW10: April 2016, Noumea, New Caledonia
Day 3 Session 3 Parameter estimation – Catchability and Selectivity
A standardized CPUE analysis of the Japanese distant-water skipjack pole-and-line fishery in the western and central Pacific Ocean (WCPO), (SA.
Current developments on steepness for tunas:
ANALYSIS OF SKIPJACK CATCH PER UNIT OF EFFORT (CPUE) Mark N
Longline CPUE standardization: IATTC 2006
Spatial strata and age groupings
SESSION 4 Annual Catch Estimates Introduction/Objectives – WCPFC Obligations Seventh Tuna Data Workshop (TDW-7) April 2013 SPC, Noumea, New Caledonia.
TDW-11: 24-28th April 2017, Noumea, New Caledonia
SESSION 4 Annual Catch Estimates Introduction/Objectives – WCPFC Obligations Sixth Tuna Data Workshop (TDW-6) April 2012 SPC, Noumea, New Caledonia.
Steve Brouwer Oceanic Fisheries Programme Pacific Community
Extract from the REPORT OF THE 6th MEETING OF THE CCSBT STOCK ASSESSMENT GROUP AND THE 10th MEETING OF THE SCIENTIFIC COMMITTEE Taipei, 28 Aug – 9 Sep.
Output of LL1 CPUE analysis
SEAPODYM.
Research outline for CPUE data used in WCPO stock assessments
John Hampton & Shelton Harley SPC Oceanic Fisheries Programme
Training in Logsheet Data Quality
Stock Assessment section – use of tuna data
U.S. NMFS contracts the CIE to review assessments
Presentation transcript:

CPUE analysis methods, progress and plans for 2011 Simon Hoyle

Introduction Methods used in 2010 Work with operational data Background information about problems in CPUE and development needs Plans for 2011 development Plans for 2011 assessments

Data JP DWLL aggregated data, 1952-present

Spatial stratification Fig. 3

JP effort

JP catch

Nominal CPUE

JP spatial strata

Standardization Linear model on log(catch), normally distributed error assumed Terms for time, location (5° lat x long), HBF (set depth), effort (hooks),

Bigeye 2010 approach vs nominal

Yellowfin 2010 approach vs nominal

Regional scaling CPUE index a measure of density. Doesn’t account for size of each region and magnitude of CPUE and therefore abundance.

Nominal CPUE varies among regions (YFT)

But CPUE GLM indices are normalized to average 1

Regional re-weighting Widest spatial distribution of JP LL fleet, before shift in fishing effort to BET

Sum the 5° indices by region to get relative abundance

Region specific CPUE index = relative abundance between regions i.e. region scaling factors. Regional scaling – weighting each region in the model

Then adjust the average CPUE indices for the same period to the right level

Regional scaling assumptions Assume constant LL q’s between regions. Assumes equivalent vertical distribution over entire model domain. Both assumptions are unreliable

15 N 5 N 5 S 15 S Longitude Depth m

Regional scaling BigeyeYellowfin BigeyeYellowfin

Japanese LL effort distribution (1*1 deg) Number of hooks

Summary Assessments critically dependent on JP LL CPUE data: regional structure, regional scaling, relative abundance. Assume constant catchability (q) over history of fishery (for standardised CPUE). Contraction of fishing range by JP fleet.

Analyses of Japanese operational CPUE data for bigeye tuna Simon Hoyle, Hiroshi Shono, Hiroaki Okamoto, & Adam Langley WCPFC-SC SA-WP-02_Bigeye_Operational_CPUE

Origin of this work Japan (NRIFSF) and SPC arranged collaboration, to use set-by-set longline data compiled from logsheets submitted by Japanese longline fishermen, with aims of: – standardizing Japanese longline CPUE of bigeye tuna; and – Estimating the historical trend of Japanese longline catchability of bigeye tuna.

Some poorly understood observations Standardized indices in equatorial areas decline less than nominal Inconsistencies with other assessment data – Stable or increasing bigeye longline CPUE – Yellowfin CPUE decline greater than expected

Need Primary need is to understand the processes driving CPUE trends For understanding, operational data are far more useful than aggregate data

Analyses carried out Data preparation & summaries Catchability analyses Regional scaling Comparisons of indices with those estimated from aggregated data

Data summaries 5x5 squares fished through timeCPUE by species through time

Summaries unique to operational data Proportion of sets with zero catch (by species, time, and region)

Fishing patterns in region 3 North of 10N, effort since 1995 has caught more albacore and less bigeye This pattern is associated with individual vessels with low bigeye catch rates

Equatorial modelFull region 3

Region 3 models Different CPUE trends in equatorial region and north of 10N – Probably because of arrival of more albacore, and the albacore-targeting fleet, after 1995 – i.e. targeting (not abundance) affecting CPUE Much higher bigeye catch rates (& abundance) south of 10N Indices should focus on core area

Regional scaling BET: yellow is high CPUE

Catchability analyses Results indicated two important influences on catchability – Changes in individual vessels through time – Changes in targeting through time

Changes in individual vessels Equatorial model Red CPUE series includes vessel effect Difference about 19% over 30 years

HBF effects HBF effects region 1 to 4 Equatorial regions have higher CPUE at lower HBF (shallower sets) R1 R2 R3 R4

Data aggregation Long-term trend Short-term trends

Conclusions in 2010 Very encouraging collaboration on operational CPUE of Japanese longline data Further development high priority for stock assessments – Primary need is to understand the processes that affect CPUE Changes in targeting and changes associated with individual vessels both affect catchability through time For 2010, indices for region 3 focused on the equatorial area 0-10N

Background about problem areas Data weighting and aggregation Targeting changes and vessel behavior Regional scaling ‘Filling the gaps’ – assumptions about unfished areas

Weighting & aggregation Data weighting affects results (Campbell 2009) – Important where CPUE varies in space, and effort concentration changes – Bigeye CPUE varies in space, effort is contracting & concentrating into high CPUE areas Operational index trends positively biased – More weight to areas with more sets Aggregated indices also need investigation – Same weight to all strata, but less fished areas have fewer strata – Increasing concentration at scales smaller than 5x5 Change approach to weighting

‘Filling the gaps’ Exclusion of fleet from EEZ waters. Contraction of JP fleet. GLM lat/long variable generally can deal with this. However, potential biases in index if spatial (lat/long) differences in CPUE trend, esp. in case of some cells not being included in analysis. Missing cells – assumed same CPUE trend. May not be valid.

Changes in targeting – YFT vs BET Increasing focus of longliners on bigeye tuna through time Region 3 YFT catch rates have declined, while BET have not We cannot estimate BET/YFT targeting – YFT and BET CPUE positively correlated at the set level – HBF is not a consistent target indicator Targeting substantially affects CPUE We need to understand the processes better

Results from Langley 2007 Effort appears more aggregated – Collaboration between vessels – Better information Increasing proportion of sets in locations with high BET CPUE Increasing probability of moving after sets with low BET CPUE, but not low YFT

Generalize fishing process: individual trip Fishing location “cluster” Movement (60+ km) Intermediate set Entry Exit

Higher BET CPUE within a cluster (a). Lower rate of decline in BET CPUE within cluster (b). More sets within a cluster (c). Increasing proportion of sets in locations with high BET CPUE = “hyperstability”

Plans for 2011 Development: Operational data analyses in Shimizu, Japan (if possible) – Find approach to deal with data weighting issue – Catchability analyses for YFT – Comparative analyses with oceanographic data – Derive indices , for both BET & YFT Assessments 2011 – Use operational data indices – TW indices (regions 4 and 6)? Regional scaling?