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![Page 1: 1 Optimal fishing policies that maximize sustainable ecosystem services Hiroyuki Matsuda (Yokohama Nat’l U), Mitsutaku Makino (Jpn Fish Agency) Koji Kotani.](https://reader035.fdocuments.in/reader035/viewer/2022062305/56649e5e5503460f94b577a1/html5/thumbnails/1.jpg)
1
Optimal fishing policies that maximize sustainable ecosystem services
Hiroyuki Matsuda (Yokohama Nat’l U),
Mitsutaku Makino (Jpn Fish Agency)
Koji Kotani (International Univ of Jpn)
![Page 2: 1 Optimal fishing policies that maximize sustainable ecosystem services Hiroyuki Matsuda (Yokohama Nat’l U), Mitsutaku Makino (Jpn Fish Agency) Koji Kotani.](https://reader035.fdocuments.in/reader035/viewer/2022062305/56649e5e5503460f94b577a1/html5/thumbnails/2.jpg)
2
Overview
Requiem to Maximum Sustainable Yield theory Adaptive management is useful for uncert
ain, dynamic stocks, but… Yield is a small part of ecosystem services MS Ecosystem Services is more prudent a
nd enhance biodiversity To ecosystem comanagement Comprehensive indicator of biodiversitya
![Page 3: 1 Optimal fishing policies that maximize sustainable ecosystem services Hiroyuki Matsuda (Yokohama Nat’l U), Mitsutaku Makino (Jpn Fish Agency) Koji Kotani.](https://reader035.fdocuments.in/reader035/viewer/2022062305/56649e5e5503460f94b577a1/html5/thumbnails/3.jpg)
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Requiem to Maximum Sustainable Yield Theory
Ecosystems are uncertain, non-equilibrium and complex.
MSY theory ignores all the three. Does MSY theory
guarantee species persistence?- No!!
Stock abundance
surp
lus p
rodu
ctio
n
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Unconstrained MSY that maximizes the total yield from the community
(Matsuda & Abrams 2006 Ecol Appl)
dN/dt = (r – C.N – e)N, Y = e.(pN – c) We choose fishing effort ei independent
ly; 6-species systems including 2 prey random matrix with 50% probabilities; we seek r having a positive equilibrium; price p is 0-1 for prey, 0-10 for predator
s
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Examples of biological community at MSY (Matsuda & Abrams 2006 Ecol. Appl.)
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(b)
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(a)
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(c)
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Solution maximizing total yield from community
MSY solution often reduces species and links;
1 2
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(d)
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(e)
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Conclusion of MSY from food web
MSY theory does not guarantee species coexistence
Fisheries must take care of biodiversity conservation explicitly
= Foodweb constraint to reconciling fisheries with conservation
e.g., Consider ecosystem services!
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Overview
Requiem to MS Yield theory Adaptive management is useful for uncert
ain, dynamic stocks, but… Yield is a small part of ecosystem services MS Ecosystem Services is more prudent a
nd enhance biodiversity To ecosystem comanagement Comprehensive indicator of biodiversity
![Page 8: 1 Optimal fishing policies that maximize sustainable ecosystem services Hiroyuki Matsuda (Yokohama Nat’l U), Mitsutaku Makino (Jpn Fish Agency) Koji Kotani.](https://reader035.fdocuments.in/reader035/viewer/2022062305/56649e5e5503460f94b577a1/html5/thumbnails/8.jpg)
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Rules of fishing effort that depend on the estimate of stock abundance
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1
0 200 400 600 800 1000 1200Estimate of stock abundance N
Fis
hin
g m
ort
alit
y F
ABC rule
Constant catch
Constant escapement
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Merits of adaptive stock management
Constant harvest (CH) amount will drive stock collapse, even CH ratio too
Constant escapement results in a huge variation of catch and vulnerable to stock measurement errors.
Adaptive management (“ABC rule”) results in more stable catch, is robust against measurement & process errors.
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If prey is exploited and fishing effort is feedback control, ...(Matsuda & Abrams
in prep.)
no adaptation (C is constant)dE/dt = U(N-N*)
1bfCN
hCNdP d gP Pdt
dN/dt=0dP/dt=0
sardine N
predator P fishery E
11
dN r N P qCENdt
fCNNK hCN
N
P
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Toward ecosystem approach
Single stock monitoring is dangerous Target stock level is much more sensitive
than we have considered in single stock models.
We must monitor not only stock level of target species, but also the “entire” ecosystem.
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Overview
Requiem to MS Yield theory Adaptive management is useful for uncert
ain, dynamic stocks, but… Yield is a small part of ecosystem services MS Ecosystem Services is more prudent a
nd enhance biodiversity To ecosystem comanagement Comprehensive indicator of biodiversity
![Page 13: 1 Optimal fishing policies that maximize sustainable ecosystem services Hiroyuki Matsuda (Yokohama Nat’l U), Mitsutaku Makino (Jpn Fish Agency) Koji Kotani.](https://reader035.fdocuments.in/reader035/viewer/2022062305/56649e5e5503460f94b577a1/html5/thumbnails/13.jpg)
132006/5/22 13
Ecosystem services and well-being(MA2005)
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Ecosystem Services and Natural Capital
Goods (Resource of Agriculture etc.)Goods (Resource of Agriculture etc.) Ecosystem services (Air, Water)Ecosystem services (Air, Water) Amenity, and intrinsic values are estiAmenity, and intrinsic values are esti
mated to be in US$16-54 trillion per mated to be in US$16-54 trillion per year, most of which is outside the mayear, most of which is outside the market rket
![Page 15: 1 Optimal fishing policies that maximize sustainable ecosystem services Hiroyuki Matsuda (Yokohama Nat’l U), Mitsutaku Makino (Jpn Fish Agency) Koji Kotani.](https://reader035.fdocuments.in/reader035/viewer/2022062305/56649e5e5503460f94b577a1/html5/thumbnails/15.jpg)
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Overview
Requiem to MS Yield theory Adaptive management is useful for uncert
ain, dynamic stocks, but… Yield is a small part of ecosystem services MS Ecosystem Services is more prudent a
nd enhance biodiversity To ecosystem comanagement Comprehensive indicator of biodiversity
![Page 16: 1 Optimal fishing policies that maximize sustainable ecosystem services Hiroyuki Matsuda (Yokohama Nat’l U), Mitsutaku Makino (Jpn Fish Agency) Koji Kotani.](https://reader035.fdocuments.in/reader035/viewer/2022062305/56649e5e5503460f94b577a1/html5/thumbnails/16.jpg)
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Ecosystem services V(N, C)
2008/3/2 16
V(N, C) = Y(C) – cE + S(N)
Provisional Service (Fisheries Yield) … Y(C) Fishing Cost… cE Utility of standing biomass… S(N) C… catch; E… fishing effort; N… stock biom
ass
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Stock abundance N
Regulating services S(N)= SN2/(B2+N2)
(S, B) = (100,10)
(S, B) = (50,50)
2008/3/2 17
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Mathematics Stock dynamics … dN/dt = (r – aN)N – C, Catch and yield … C = qEN, Y(C) = pqEN, Regulating service … S(N) = SN2/(B2+N2), Equilibrium … N*(E) = (r – qE)/a Service at N* … V*(E) = pqEN* – cE + S(N*) Optimal effort Eopt satisfies that V*/E = 0 Maximum Sustainable Ecosystem Service
Eopt = (pqr – ac)/2pq2
2008/3/2 18
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19Fishing effort E
Maximum Sustainable Ecosystem Service
(S, B) = (100,10)
(S, B) = (50,50)
(S, B) = (0,-)
2008/3/2 19
Stock abundance N
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ck N
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atc
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ing
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MSY vs MSES with process uncertainties
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ck N
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MSES from food webs
Community dynamics …dNi/dt = (ri + ajiNj – qiEi)Ni
Yield from foodweb… Y(E) = Ei(piqiNi – ci)
Total ecosystem services...V(E) = Y(E) + Si(Ni)
Si(Ni) = SiNi
2/(Bi2+Ni
2)
We obtained EMSES ↑ Y(E) and EMSY ↑V(E)
2008/3/2 21
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Resultant food webs and fishing efforts from 1000 randomly constructed six species systems
No. of species
No. of extant species using MSY policy
No. of exploited
species using MSY policy
No of extant species using MSES policy
No of exploited species using MSES policy
0 0 0 0 9
1 0 204 0 96
2 206 792 13 318
3 531 4 43 337
4 236 0 31 201
5 25 0 8 35
6 2 0 905 4
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MSES saves fishing efforts
2008/3/2 24
Ban-on-Fishing
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Overview
Requiem to MS Yield theory Adaptive management is useful for uncert
ain, dynamic stocks, but… Yield is a small part of ecosystem services MS Ecosystem Services is more prudent a
nd enhance biodiversity To ecosystem comanagement Comprehensive indicator of biodiversity
![Page 26: 1 Optimal fishing policies that maximize sustainable ecosystem services Hiroyuki Matsuda (Yokohama Nat’l U), Mitsutaku Makino (Jpn Fish Agency) Koji Kotani.](https://reader035.fdocuments.in/reader035/viewer/2022062305/56649e5e5503460f94b577a1/html5/thumbnails/26.jpg)
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1. The objectives … are a matter of societal choice.2. Management should be decentralized to the lowest …level. 3. ... managers should consider …adjacent …ecosystems. 4. … usually …manage …in an economic context. Any such ecosystem-management programme should: 5. Conservation of ecosystem structure and functioning… shoul
d be a priority target of the ecosystem approach. 6. Ecosystem …managed within the limits of their functioning.7. … undertaken at the appropriate spatial and temporal scales. 8. Recognizing the varying temporal scales and lag-effects…,
objectives …should be set for the long term. 9. Management must recognize the change is inevitable. 10. The ecosystem approach should seek the appropriate balance
between… conservation and use of biological diversity. 11. …should consider all…, including scientific and indigenous
and local knowledge, innovations and practices. 12. …involve all relevant sectors of society and …disciplines.
12 Principles of Ecosystem Approach of CBD
The Ecosystem Approach is a social strategy that links biological, social and economic information, and aims to achieve a socially acceptable balance between nature conservation and the use and sharing of benefits from ecosystems.
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Fishers can monitor “their” marine ecosystem
Monitoring activities are critically important to increase the yield Y(E) and to sustain the utility of standing biomass S(N). Government should play an important role in these monitoring activities. However, in reality, it is almost impossible for the government to monitor all the detailed ecosystems along the coast and within exclusive economic zones (EEZ). Therefore, the knowledge of fishers and data from fishery activities should be fully utilized.
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Most of keystone species are caught and recorded by local
fishers org.s!Sustainable fisheries play
roles of “umbrella species” like top predators!
Coastal Foodweb at Shiretoko Heritage
Draft food web by SC
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Fisheries catch statistics in Shiretoko Area
tons
Very informative time-series data for monitoring the changes in ecosystem structure/functions
Made by Mitsutaku Makino
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Reality of MSES Our analyses also indicate that yield-maximizing
fisheries would invoke the loss of a significant fraction of species in the web. It will inevitably lead to the degradation of S(N), and easily set off the benefit from Y(C), and ultimately reduce the total ecosystem services, V(E).
To avoid these situations, government has to monitor the rest of the ecosystem, and regulate the yield-maximizing fisheries in a top-down way. The reality is, again, these costs would be beyond the budget of many countries, especially developing countries. To sum up the above discussions, yield-maximizing, economically-efficient fisheries are rational for enjoying fishery rent, but not always so in sustaining total ecosystem services for society.
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Fishers’ knowledge may sustain ecosystems
From the viewpoint of sustaining ecosystem services, we encourage responsible fisheries targets for a wide range of species with a variety of gear.
Local fishers often have accumulated the catch data of these species for over 50 years. Responsible fisheries can significantly contribute to the sustainability of ecosystem services if we evaluate the catch data.
A fisheries management approach in which government and local fishers share the responsibilities and authorities for the use of sustainable resource is called fisheries comanagement, the strongest argument against the conventional top-down approach (Makino and Matsuda 2005).
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Forestation activities by local people (http://www.jf-net.ne.jp/hkyubetsu/sigen.htm)
Local legend says
“Forests are the roots of coastal fish”(http://www.jf-net.ne.jp/amhiranaigyokyo/)
Voluntary Activities (1)
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Spawning ground
Since 2005
Bottom trawling is totally prohibited in the coastal area
R1: Voluntary regulation of walleye pollock
177 boats fished walleye pollock in 1995Decreased to 86 boats in 2004 (49% reduction)
– Compensation to retired fishers by Fisheries Organization
Fishing ban during Mar 20-end since 1995Fishing ban area expanded in 2005 Since 1995
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Role of the government
To avoid these situations, government has to monitor the rest of the ecosystem, and adaptively regulate the yield-maximizing (i.e. commercial) fisheries, often in a top-down way.
The reality is, these costs would be beyond the budget of many countries, esp. developing countries.
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From fisheries comanagement to ecosystem comanagement
Fisheries comanagement will not always lead to the ecosystem management: It is likely that VMSES > VMSY and EMSES < EMSY
In order to increase the total ecosystem services, interests from other sectors than fisheries, such as an environmental ministry or non-government organizations (NGOs), should be included in the decision-making arena (Makino 2005).
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Overview
Requiem to MS Yield theory Adaptive management is useful for uncert
ain, dynamic stocks, but… Yield is a small part of ecosystem services MS Ecosystem Services is more prudent a
nd enhance biodiversity To ecosystem comanagement Comprehensive indicator of biodiversity
![Page 37: 1 Optimal fishing policies that maximize sustainable ecosystem services Hiroyuki Matsuda (Yokohama Nat’l U), Mitsutaku Makino (Jpn Fish Agency) Koji Kotani.](https://reader035.fdocuments.in/reader035/viewer/2022062305/56649e5e5503460f94b577a1/html5/thumbnails/37.jpg)
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Convention on Biological Diversity (CBD) CoP10, Nagoya, Japan, 2010
CBD CoP10 is important because of the 2010 Biodiversity Target (CoP6). Host nation Japan must keep leadership of further goals.
“Parties commit themselves to […] achieve by 2010 a significant reduction of the current rate of biodiversity loss.”
I expect Ministry of Environment to make Comprehensive Environmental Assessment with indicators
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Draft framework of marine biodiversity by Matsuda
DP1:Fisheries & exploitation• Overfishing• By-catach• Aquaculture• Bottom trawling• Catch of marine mammals
Driving forces/Pressures State/Impacts Response
DP2 Civil engineering• Fluvial sediment• Reclamation, artificial
shore and breakwater• Gravel dipping
SI1 Loss of species richness• Mean trophic levels• Fish stock biomass• Mammals, birds & turtles
R1 Sustainable use• Catch regulation• Ecolabels• Stock rehabilitation p
rogram
SI2 Habitat loss/degradation• Sand beach• Sea grass/weed beds• Tidal flat• Coral reefs
DP3 Pollution and debris• Eutrophication• Oil spilling• Exotic species• Chemicals (TBT)
SI3 Material cycling• Red tide, blue tide• Imposex of snails
R2 MPAs by• International MPAs• National parks• Voluntary MPAs• Nature restoration pro
jects
R3 Env. regulations• Env. Impact Assess.• BOD emissions• TBT regulationSI4 Genetic pollution
• SalmonidsDP4 Climate change• Global warming• pH decrease
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DP3 Exotic marine species
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DP3: PCDDs, PCDFs and Co-PCBs in Tokyo Bay: Sources and Contribution,
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SI1: Fishing down (MA 2005)
In Japan??? F-MAP’s mission?
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SI1: Catch and mean trophic levels in Japan
Fishing ground changed decadally.
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10
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50
60
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1997 1998 1999 2000 2001 2002 2003
TAC
AB
CC
atch
1000
0ton
s,
,(
) マイワシ
SI1: trend in catch and stock of Red Sea Bream and Japanese sardine
Stock (1000 tons)
Harvest rate
CatchCatch of wild larvaeSeed release
Stoc
k (1
000
tons
)
Har
vest
rat
e
Caa
tch
(100
0 to
ns)
No.
indi
vudu
als
(10,
000)
Red Sea Bream (West Sea of Japan/Southeast China Sea)
Stoc
k (1
000
tons
)
Har
vest
rat
e
Stock (1000 tons) Harvest rate
Japanese sardine (Pacific stock)Japanese sardine (total)
ABCTACCatch
http://abchan.job.affrc.go.jp/digests20/index.html
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SI2: Reduction of sea grass/weed bed in Seto Inland Sea
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SI2: Trend and volume of suspended load
要引用許可
105 m3
104 m3
103 m3
>1m increase
>1m decrease
www.nilim.go.jp/lab/dbg/pdf/200806_fac.pdf
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SI3: Imposex of Babylonia japonica by TBT/TPT ( Horiguchi et al 2006 Env Health Pers )
Fecundity (g) of cultured B. japonica Release of B. japonica juveniles (105 ind.)Catch (tons)
Horiguchi, T., Kojima, M., Hamada, F., Kajikawa, A., Shiraishi, H., Morita, M., Shimizu, M.: Impact of tributyltin and triphenyltin on ivory shell (Babylonia japonica) populations. Environ. Health Perspectives 114: 13-19, 2006.
Babylonia japonica
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Spawning ground
Since 2005
Bottom trawling is totally prohibited in the coastal area
R1: Voluntary regulation of walleye pollock
177 boats fished walleye pollock in 1995Decreased to 86 boats in 2004 (49% reduction)
– Compensation to retired fishers by Fisheries Organization
Fishing ban during Mar 20-end since 1995Fishing ban area expanded in 2005 Since 1995
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R1: The number of registered MSCs in the World and Japan
WorldJapan
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R2: MPA Construction to protect spawning/breeding area (by public
expenses)
(Sited from Kyoto Institute of Oceanic and Fishery Science HP)
牧野光琢氏
2 図 京都府沖合海域における各施策の経年変化
0
20
40
60
80
100
120
67 69 71 73 75 77 79 81 83 85 87 89 91 93 95 97 99年度
Phase1 Phase4Phase3Phase2
MPA Construction (km2)
Temporal Fishing Ban(%)
Fiscal Year
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R2:Sandfish fishery mgmt at Akita Pref.
Mgmt Method: -Complete ban of fishing for
three years (Sep. ’92 – Aug. ’97)
-Minimum size limit-Annual catch limit-Gear, ground and season limit-Restoration of breeding
ground-Fish seeds release -pooling system of fishery
income
Mapmap Ver.6.0
www.pref.akita.jp
Arctoscopus japonicusMgmt actors:Local fishermen,Local research station, etc.
Cat
ch (
tons
)
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Conclusion
Responsible fisheries may play roles of umbrella species that use a small part of healthy ecosystem services, and give many data of utilized resources…
Fishing efforts that maximizes the total ecosystem services are usually much smaller than those for maximum sustainable yield.
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Abstract Classic theory seeks MSY from target species
ignores uncertainty, fluctuation, species interactions.
MSY do not guarantee coexistence of species. Ecosystems provide supporting, provisioning (
fisheries yields), regulating, and cultural services.
The stock biomass maintains these services, and regulating services >> fishery yields.
We define maximum ecosystem service (MSES) in a single species model with and without uncertainties and in multiple species models.
In any case, fishing efforts for MSES are usually much smaller than those for MSY.
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Overview
Requiem to MS Yield theory Adaptive management is useful for uncert
ain, dynamic stocks, but… Yield is a small part of ecosystem services MS Ecosystem Services is more prudent a
nd enhance biodiversity To ecosystem comanagement Comprehensive indicator of biodiversity
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Overview
Requiem to MS Yield theory Adaptive management is useful for uncert
ain, dynamic stocks, but… Yield is a small part of ecosystem services MS Ecosystem Services is more prudent a
nd enhance biodiversity To ecosystem comanagement Comprehensive indicator of biodiversity
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Regulating services S(N)= SN2/(B2+N2)
(S, B) = (100,10)
(S, B) = (50,50)
2008/3/2 55
Stock abundance N
Unsustainable Fisheries
Maximum Sustainable Yield
No take zone