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Evolutionary fisheries management

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Evolutionary Fis Evolutionary Fis Evolutionary Fis

Mikko Heino (University of Bergen N Mikko Heino (University of Bergen, N Evolution and E Evolution and E Ulf Dieckmann (Evoluti Ulf Dieckmann (Evoluti

Fishing as a Driving Force of Evolution Fishing as a Driving Force of Evolution

 A key determinant of life-history diversity is the trade-off between fitn

 A key determinant of life-history diversity is the trade-off between fitn

 Example: growing big requires sacrificing early reproduction in f

 Example: growing big requires sacrificing early reproduction in f Benefits of growing big:

outgrowing natural predators

big fis

Benefits of growing big:

outgrowing natural predators

big fis

Costs of growing big:

loss of reproduction in early life

chanc

Costs of growing big:

loss of reproduction in early life

chanc

Fishing reduces the benefits and increases the costs of gro

Fishing reduces the benefits and increases the costs of gro

Evidence Evidence

 Trends towards

 Trends towards

 In agreement

 In agreement

 Other explana

 Other explana

 Method develope

 Method develope

 Applied now i

 Applied now i

 Most cases su

 Most cases su

Period of heavy exploitation coincided with Period of heavy exploitation coincided with declining age at maturation in northern cod declining age at maturation in northern cod (Ol t l 2004)

(Olsen et al. 2004)

Consequenc

J

Consequenc

ør

q

rge

 Fish adapted to

en

 Fish adapted to

nse

 tolerate more

en

 tolerate more

n e

 may be more

et

 may be more

al

 are less produ

. 2

 are less produ

20

 are on a erag

07

 are on averag

7 S

 Fisheries ind ce

Sc

 Fisheries-induce

cieenccee

Evolutionary Evolutionary y

 W d t

 We need to asse

 i fi h

 ongoing fishe

Fisheries induced evolution

g g

 iti ti t

Fisheries-induced evolution

 mitigating act

→ ecosystem services

g g

 N f k

→ ecosystem services

 New framework:

S ti i

Q tif

th

Supporting services

Quantify

the

g

P i i i i y

population un

Provisioning services

population un

g

Jørgensen

Regulating servicesg g

Jørgensen

Cultural services

Cultural services

References References

H i M Di k U d G d O R 2002 M i L

Heino, M., Dieckmann, U., and Godø, O. R. 2002. Measuring , , , , , g Laugen probabilistic reaction norms for age and size at maturation

g

Evolutio probabilistic reaction norms for age and size at maturation. Evolutio

Evolution 56: 669–678. conseq

Evolution 56: 669 678. conseq

Jørgensen, C., Enberg, K., Dunlop, E. S., et al. 2007. Managing g , , g, , p, , g g manage evolving fish stocks Science 318: 1247 1248 Olsen evolving fish stocks. Science 318: 1247–1248. Olsen,

indicativ indicativ N t

Nature

sheries Management sheries Management sheries Management

Norway; Institute of Marine Research Norway;

Norway; Institute of Marine Research, Norway;

Ecology Program IIASA) Ecology Program, IIASA)

ion and Ecology Program IIASA) ion and Ecology Program, IIASA)

©© NNaasjon

ness gains in early and late life

na

ness gains in early and late life lb

favour of growth

ib

favour of growth lio

sh are highly fecund

ote

sh are highly fecund eke

ce of dying before reproduction

et,

ce of dying before reproduction , N

owing big → fishing favours faster life

No

owing big → fishing favours faster life orwwaay

earlier maturation are ubiquitous in heavily exploited fish stocks earlier maturation are ubiquitous in heavily exploited fish stocks

with predicted fisheries induced evolution with predicted fisheries-induced evolution ations are possible

ations are possible

ed at IIASA helps to disentangle explanations (Heino et al 2002) ed at IIASA helps to disentangle explanations (Heino et al. 2002)

n 13 species representing >30 cases n 13 species, representing >30 cases

uggest that fisheries induced evolution has occurred uggest that fisheries-induced evolution has occurred

ces ces

fishing:

fishing:

overfishing overfishing

sensitive to long term fluctuations?

sensitive to long-term fluctuations?

uctive uctive

ge smaller ge smaller

ed e ol tion can diminish the al e of fish as a reso rce ed evolution can diminish the value of fish as a resource

y Impact Assessment y Impact Assessment

y p

t d b fit ess costs and benefits:

i i d d l ti

ries-induced evolution iions

th

E l ti I t A t (E IA)

the

Evolutionary Impact Assessment (EvoIA) y p ( )

f fi h i i d d l ti

tilit

f fi h consequences of fisheries-induced evolution on utility q

y

of a fish nder alternative management

actions

including the status quo nder alternative management actions, including the status quo g g n et al 2007 Laugen et al 2012

n et al. 2007, Laugen et al. 2012

A T E lh d G H Whitl k R t l 2012 n, A. T., Engelhard, G. H., Whitlock, R., et al. 2012. , , g , , , ,

onary impact assessment: Accounting for evolutionary onary impact assessment: Accounting for evolutionary

uences of fishing in an ecosystem approach to fisheries uences of fishing in an ecosystem approach to fisheries

t Fi h d Fi h i i

ement. Fish and Fisheries, in press

E M Heino M Lilly G R et al 2004 Maturation trends E. M., Heino, M., Lilly, G. R., et al. 2004. Maturation trends ve of rapid evolution preceded the collapse of northern cod ve of rapid evolution preceded the collapse of northern cod.

428 932 935 428: 932–935.

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