Simple Approaches to Data-Poor Stock Assessment
Rainer Froese
rfroese@ifm-geomar.de
March 9, 2011, Troutdale, Oregon
Overview
• Some background
– Fecundity – Size matters – Recruitment
• Options for Management
– Length-only
– Semelparous species
– Revisiting Schaefer
– If biomass is known
NO RELATIONSHIP BETWEEN FECUNDITY
AND ANNUAL REPRODUCTIVE RATE IN BONY FISH
Rainer FROESE, Susan LUNA
ACTA ICHTHYOLOGICA ET PISCATORIA (2004) 34 (1): 11–20
Maximum annual reproductive rate versus mean (solid dots) and minimum (open dots) annual fecundity.
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Fish and Fisheries, 2004, 5, 86–91
Keep it simple: three indicators to deal with overfishing
Rainer Froese
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• Reducing catch to F
msyis good but insufficient
• Stock size may increase seven-fold if fish are caught after multiple spawning, at around 2/3 of their maximum length
• Large stock size means low cost of fishing
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Age-structure of North Sea Cod, with same catch but different minimum size
For a given catch, the impact on the stock is least if fish are caught at Lopt
Current
Fmsy
Fmsy & Lopt
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Same catch, better age structure
Stock size can increase seven-fold
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The Hockey-Stick
(Barrowman & Myers 2000)
S R
1
max
2
R
R
Assumptions:
a) Constant R/S at low S
b) Constant R at high S
The Smooth Hockey-Stick
(Froese 2008)
) 1
ln(
ln R A e
eA S
) 1
(
maxmax
R S
e R
R
Assumptions:
a) Practically constant R at high S
b) Gradually increasing R/S at lower S
where A = ln Rmax
Parameters and accounted variance not significantly different
Model α low up Rmax low up r2
B&H 3.67 2.60 4.73 24.9 17.3 36.0 0.834
Froese 3.40 2.64 4.15 17.4 13.5 22.6 0.843
Ricker 3.22 2.64 3.81 19.8 16.5 23.9 0.846
Example Striped bass Morone saxatilis
Extrapolation VERY different
Bold line is Smooth Hockey-Stick with n = 414, α = 4.5, Rmax = 0.85 Dotted line the Ricker model with n = 414, α = 3.1, Rmax = 1.4. Data were normalized by dividing both R and S by Rmax for the respective stock.
Example: 12 stocks of Atlantic cod Gadus morhua
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Number of replacement spawners versus number of parents for 48 Pacific
salmon populations. The fitted smooth hockey stick has a slope of 4.2 (3.6 – 5.2).
Assesment and Management Options
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If nothing is known about the stock
Management:
•Get an estimate of maximum length (interviews; old photos; FishBase)
•Get an estimate of length at first maturity (examine specimens; FishBase)
•Set minimum length in catch and/or start of fishing season such that >90% of the specimens had a chance to reproduce before being caught
•Give incentives to catch only fish with a length of 2/3 of their maximum length
•
Justification:
•Overfishing is theoretically impossible if all fish have a chance to reproduce before capture (Myers and Mertz, 1998). Impact of fishing on cohorts is
minimized at about 2/3 of maximum length.
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If L ∞ is known
Assessment
•Get length at first capture and mean length in catch
•Derive reference length where F ~ M from
•Derive reference length where F
msy~ ½ M from
Management
•Set minimum length in catch to L
F~M, if larger than length where 90% are mature, else use that length
•Set target length in catch to L
Fmsy 1516
If species die after spawning (salmons, eels, cephalopods)
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If Catch and Effort are Known
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If MSY and B msy are known
(Data-rich Management)
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Generic Harvest Control Rules for European Fisheries
Rainer Froese, Trevor A. Branch, Alexander Proelß, Martin Quaas, Keith Sainsbury & Christopher Zimmermann
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Rules for sustainable and profitable fisheries based on 1) economic optimization of fisheries
2) honoring international agreements
3) true implementation of the precautionary principle 4) learning from international experiences
5) ecosystem-approach to fisheries management 6) recognizing the biology of European fish stocks
• If these rules were applied, catches could increase by 63%
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Harvest Control Rule Schema
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Fisheries in 2007
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North Sea Herring 1960 - 1978
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North Sea-Herring 1979 - 2008
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ICES F-based Mangement
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North Sea Herring Once More
F-based Management would not have prevented the collapse of herring. 26
Critique of Planned F-based Management
• F
msyis taken as target, not limit, thus violating UNFSA and the precautionary principle
• Fishing at F
msyis less profitable than at F
mey• Fishing at F
msyresults in substantially smaller stocks, violating the ecosystem approach
• Fishing at F
msyresults in strongly fluctuating catches with high uncertainty for the industry
• Fishing at F
msyprovides strong incentives for overcapacity
• Fishing at TAC = 0.9 MSY solves these problems
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Thank You
Rainer Froese
IFM-GEOMAR, Kiel, Germany rfroese@ifm-geomar.de
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