Status of Exploited Marine Fishes and Invertebrates in German Marine Waters Rainer Froese, GEOMAR Cluster Meeting ökosystemgerechte Fischerei Bundesamt.

Slides:



Advertisements
Similar presentations
An example of harvest rule control for recovery the jack mackerel population Cristian Canales- IFOP- Chile.
Advertisements

The Common Fisheries Policy State of Resources and Ecosystems Rainer Froese, GEOMAR, Germany 10 December 2014 Sustainable Fisheries Internal Seminar S&D.
Fishery indicators V.Raykov,IO-BAS
Some Comments on SSB msy and Indicators of Healthy Size Structure Rainer Froese, GEOMAR WKGMSFD D3 Copenhagen, 4-5 September 2014.
Swedish University of Agricultural Sciences Status of Mediterranean and Black Sea resources in European Waters in 2013 Results for stocks in.
MSFD Indicators and Reference Points for Data-Limited Stocks Rainer Froese GEOMAR ICES MSFD Workshop, Copenhagen 13 January 2014.
Towards Healthy Stocks and Healthy Profits in European Fisheries Rainer Froese IFM-GEOMAR Presentation at Hearing „How much fish.
Proper Implementation of the MSY-Concept in the CFP European Parliament Brussels, 29 Nov 2011 Rainer Froese, IFM-GEOMAR.
The Good, the Bad, the Worrisome A Critical Look at the New Common Fisheries Policy of the EC Rainer Froese Presentation at the 2013.
Remaining Issues with the CFP Reform Rainer Froese, GEOMAR Breakfast Discussion with Fisheries Attachées 6th March 2013, WWF Office, Brussels.
Black Sea Bass – Northern Stock Coastal-Pelagic/ASMFC Working Group Review June 15, 2010.
ICES advice as of 30th June 2014 Nick Bailey, Coby Needle, Helen Dobby, Emma Hatfield Marine Scotland - Science.
Progress with Assessment of Data-Limited Stocks Rainer Froese Vilm,
New Approaches for the Management of Data-Limited Stocks Rainer Froese GEOMAR Rethinking paradigms & approaches in fisheries research ZMT, Bremen, 20 March.
Certification of Seafood Products: Vision and Reality Rainer Froese 2nd Hamburg International Environmental Law Conference September.
Fisheries Fish as Food Commercial Fisheries Trends in World Fisheries Solutions?
Pathways Towards Sustainable and Profitable Fisheries Rainer Froese IFM-GEOMAR, Kiel, Germany FC-UBC, 08 March
Barents Sea fish modelling in Uncover Daniel Howell Marine Research Institute of Bergen.
458 Policies and Their Evaluation Fish 458, Lecture 22.
Generic Harvest Control Rules for European Fisheries Rainer Froese, Trevor A. Branch, Alexander Proelß, Martin Quaas, Keith Sainsbury & Christopher Zimmermann.
Many Ways to Estimate Bmsy
Biodiversity of Fishes Stock-Recruitment Relationships Rainer Froese,
Fisheries Management T Review of Maximum Sustainable Yield Concepts and Problems.
Simple Approaches to Data-Poor Stock Assessment Rainer Froese March 9, 2011, Troutdale, Oregon.
1 Fisheries sustainability – CFP directions, MSFD descriptors and CSI Poul Degnbol Head of ICES advisory programme / ETC/W Marine and Coastal EEA/EIONET.
MSFD Indicators and Reference Points for Data-Limited Stocks Rainer Froese GEOMAR EU-BON Workshop, Leipzig 18 February 2014.
Ecological Objective 3: Harvest of commercially exploited fish and shellfish Populations of selected commercially exploited fish and shellfish are within.
Legal Governance of European Fisheries Rainer Froese Law of the Sea in the 21 st Century CAU, Kiel,
Descriptor 3 for determining Good Environmental Status (GES) under the MSFD was defined as “Populations of all commercially exploited fish and shellfish.
Fishing in National and International Waters: MSY and Beyond Rainer Froese GEOMAR, Kiel, Germany 2nd Sustainable Oceans Conference: Reconciling.
Revisiting Stock-Recruitment Relationships Rainer Froese Mini-workshop on Fisheries: Ecology, Economics and Policy CAU, Kiel, Germany.
Towards Sustainable Fisheries in Europe Rainer Froese GEOMAR, Kiel, Germany 3rd International Conference on Progress in Marine Conservation.
Life-History Traits of Fishes: A Review with Application for Mangement of Data-Poor Stocks Rainer Froese GEOMAR, Kiel,
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
F MSY is good 0.9 F MSY is better 0.9 MSY is best.
Two Promising Methods for Assessment of Data-Poor Stocks Rainer Froese, GEOMAR, Germany Daniel Pauly, FC-UBC, Canada 9 November 2014, San Francisco, USA.
Measuring the effects of a seasonal fishing closure on the abundance of Atlantic Cod (Gadus morhua) off the West Coast of Scotland Joanne Clarke 1*, David.
Oceans full of Fish? Small Steps in the Right Direction Rainer Froese GEOMAR, Kiel, Webinar Alumni Portal, 26 April.
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.
Marine Strategy Framework Directive (MSFD) Programme of Measures D2 – Non-indigenous species D3 - Commercial fish & shellfish Peter Wright Lyndsay Brown.
Summary of Atlantic Swordfish Species Working Group Discussion (see also SCI -021)
GIANNOULAKI M., SOMARAKIS S., MACHIAS A., SIAPATIS A., PAPACONSTANTINOU C. Hellenic Centre for Marine Research, PO Box 2214, Iraklion 71003, Greece Department.
And How Are the Fish? An Evaluation of Certified Seafood Rainer Froese Pew Fellows Meeting, Key Largo,
MEDITERRANEAN SWORDFISH SCI-020. Background Unique genetic stock Some mixing with the N. Atlantic one Different biological characteristics than the Atlantic.
Proxies for estimation of relative fishing mortality when biomass is unknown Rainer Froese, GEOMAR Arlene Sampang, FIN ICES ASC, Bergen, 18 September 2012.
West Atlantic bluefin tuna Executive Summary. Biology Continued progress in knowledge of bluefin biology, but the complex behaviour of this species means.
Balanced Harvesting: Not Supported by Science Rainer Froese GEOMAR, Kiel, Germany Pew Fellows Meeting, Rio Grande 16 October 2015.
Restoring Ecological Balance as a Priority for the Reform of the Common Fisheries Policy Polish Parliament (Sejm) Warsaw, 13 March 2012 Rainer Froese,
1 Federal Research Centre for Fisheries Institute for Sea Fisheries, Hamburg Hans-Joachim Rätz Josep Lloret Institut de Ciències del Mar, Barcelona Long-term.
A Common Sense Approach to Ecosystem- Based Fisheries Management In this study we show that substantial gains towards the goals of ecosystem-based fisheries.
Sustainable and Profitable Fisheries in the Future Ocean Rainer Froese GEOMAR, Kiel, Germany ISOS Lecture, 31 May 2012, Kiel 1.
CBSAC 2012 Blue Crab Advisory Report Figures. Figure 1. Winter dredge survey index of total blue crab abundance (density of males and females, all sizes.
Data requirement of stock assessment. Data used in stock assessments can be classified as fishery-dependent data or fishery-independent data. Fishery-dependent.
Artist:Glynn Gorick Fish stock status Improvements to CSI032 Henrik Sparholt ICES’ Fisheries Scientist.
Rainer Froese HOSST-TOSST Seminar 07 April 2016 GEOMAR, Kiel, Germany
Towards Sustainable and Profitable Fisheries in the Mediterranean Sea
Status and Exploitation of European Fish Stocks
Indicators for a healthy age and size structure distribution:
MSFD Descriptor 3 population age and size distribution indicative of a healthy stock Gerjan Piet & Thomas Brunel.
Many Ways to Estimate Bmsy
MSFD Indicators and Reference Points for Data-Limited Stocks
Biodiversity of Fishes Stock-Recruitment Relationships
Bestandserhaltende oder ökologisch nachhaltige Fischerei
DG Environment, Unit D.2 Marine Environment and Water Industry
Update on previous year’s discussion on Descriptor 3
ICES ASC, Bergen, 18 September 2012
Progress with Assessment of Data-Limited Stocks
MSFD Indicators and Reference Points for Data-Limited Stocks
Marine Strategy Framework Directive Descriptor 3+
Presentation transcript:

Status of Exploited Marine Fishes and Invertebrates in German Marine Waters Rainer Froese, GEOMAR Cluster Meeting ökosystemgerechte Fischerei Bundesamt für Naturschutz, Insel Vilm,

MSFD Descriptor 3 1.The level of pressure of the fishing activity, measured either as fishing mortality F relative to the one associated with the maximum sustainable yield (F msy ) or, if F is unknown, the ratio between catch and biomass, with a reference point that is compatible with F msy. 2.The spawning stock biomass SSB relative to the one that can produce the maximum sustainable yield (SSB msy ) or other suitable biomass indices. 3.The age and size distribution within the population, with the sub- indicators i.Proportion of fish larger than the mean size of first sexual maturation; ii.Mean maximum length across all species found in research vessel surveys; iii.95 % percentile of the fish length distribution observed in research vessel surveys; iv.Size at first sexual maturation [relative to historic sizes], which may reflect the extent of undesirable genetic effects of exploitation.

MSFD Descriptor 3.1: F F and Fmsy available only for fully assessed stocks (most stocks are data-limited) Natural mortality M is a proxy for Fmsy M can be estimated for all stocks Total mortality Z can be estimated from DATRAS survey data F = Z – M M / F is the chosen 3.1 indicator (positive if F < M)

How to Estimate Z Number of cohort members declines with age due to total mortality rate Z DATRAS gives CPUE by length class Get CPUE of first fully selected length class Determine length in 1, 2, 3 subsequent years Get CPUE in subsequent years for these lengths Fit regression line to ln(CPUE) Absolute slope of line is Z

Example of Estimating Z BfN_11_11_13.xlsx

Example North Sea Dab

MSFD Descriptor 3.2: SSB SSB only available for fully assessed stocks SSBmsy not given by ICES 2 * SSBpa is reasonable proxy for SSBmsy CPUE from DATRAS can be used as a proxy for SSB Proxy SSBpa can be derived as CPUE below which number of young fish in survey declines SSB / SSBmsy or the respective proxies are the chosen 3.2 indicator

Example North Sea Dab

Example of Estimating SSBpa

Example North Sea Dab

MSFD Descriptor 3.3: Age and Size Age and size distribution within the population, with the sub-indicators i.Proportion of fish larger than the mean size of first sexual maturation; ii.Mean maximum length across all species found in research vessel surveys; iii.95 % percentile of the fish length distribution observed in research vessel surveys; iv.Size at first sexual maturation [relative to historic sizes], which may reflect the extent of undesirable genetic effects of exploitation. ‘Across all species’ not suitable for population status

MSFD Descriptor 3.3: Age and Size Age and size distribution within the population, with the sub-indicators i.Proportion of fish larger than the mean size of first sexual maturation; ii.--- iii.95 % percentile of the fish length distribution observed in research vessel surveys; iv.Size at first sexual maturation [relative to historic sizes], which may reflect the extent of undesirable genetic effects of exploitation. Not visible in short time series

MSFD Descriptor 3.3: Age and Size Age and size distribution within the population, with the sub-indicators i.Proportion of fish larger than the mean size of first sexual maturation; ii.--- iii.95 % percentile of the fish length distribution observed in research vessel surveys; iv.--- Inversely sensitive to recruitment DATRAS biased towards large fish

MSFD Descriptor 3.3: Age and Size Age and size distribution within the population, with the sub-indicators i.Proportion of fish larger than the mean size of first sexual maturation; ii.-- iii.-- iv.-- Mean length in commercial catches relative to length where 90% of the females have reached maturity is the chosen indicator

Abundance in German Marine Waters Indicators selected so far operate for the stock as a whole Abundance in German marine waters is therefore selected as fourth sub-indicator for stock status Such abundance can be derived as CPUE-by- area from DATRAS Mean CPUE in time series is only available reference point

Example North Sea Cod

How Good are the Proxies? SpeciesStockNS / BS SSB / pSSB msy proxySSB / proxySSB msy M / F 2M / Z Codcod-347d*NS cod-2224*BS cod-2532*BS Herringher-47d3*NS NA her-3a22*BS Plaiceple-nsea*NS Solesol-nsea*NS NA Spratspr-2232*BS NA Most results are very similar. All proxies are on the correct side of the threshold.

Getting Summary Indicators for every Stock

Getting an Overall Indicator The overall indicator is the percentage of stocks that obtained a score >= 1

Overall Indicator

Sub-Indicator for Stock Size Low stock size determines low overall status

Sub-Indicator for Fishing Mortality Continuing overfishing prevents recovery

Sub-Indicator for Size & Age Positive bias because of reduced size & age at maturity

Sub-Indicator for Abundance Positive bias because of low reference point

Next Steps Publish results to highlight overfished status of most data-limited stocks Combine proxy indicators with analysis of catch data Establish robust system to classify relative stock size of data-limited stocks Devise simple, precautionary, ecosystem- based harvest control rules for data-limited stocks