Title: Optimal fishing policies that maximize sustainable ecosystem services
1Optimal fishing policies that maximize
sustainable ecosystem services
- Hiroyuki Matsuda (Yokohama Natl U),
- Mitsutaku Makino (Jpn Fish Agency)
- Koji Kotani (International Univ of Jpn)
2Overview
- Requiem to Maximum Sustainable Yield theory
- Adaptive management is useful for uncertain,
dynamic stocks, but - Yield is a small part of ecosystem services
- MS Ecosystem Services is more prudent and enhance
biodiversity - To ecosystem comanagement
- Comprehensive indicator of biodiversitya
3Requiem 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!!
surplus production
Stock abundance
4Unconstrained 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 independently
- 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 predators
5Examples of biological community at MSY (Matsuda
Abrams 2006 Ecol. Appl.)
- Solution maximizing total yield from community
MSY solution often reduces species and links
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6Conclusion 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!
7Overview
- Requiem to MS Yield theory
- Adaptive management is useful for uncertain,
dynamic stocks, but - Yield is a small part of ecosystem services
- MS Ecosystem Services is more prudent and enhance
biodiversity - To ecosystem comanagement
- Comprehensive indicator of biodiversity
8Rules of fishing effort that depend on the
estimate of stock abundance
Constant escapement
ABC rule
Constant catch
9Merits 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.
10If prey is exploited and fishing effort is
feedback control, ...(Matsuda Abrams in prep.)
P
- no adaptation (C is constant)
- dE/dt U(N-N)
predator P
fishery E
N
sardine N
11Toward 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.
12Overview
- Requiem to MS Yield theory
- Adaptive management is useful for uncertain,
dynamic stocks, but - Yield is a small part of ecosystem services
- MS Ecosystem Services is more prudent and enhance
biodiversity - To ecosystem comanagement
- Comprehensive indicator of biodiversity
13Ecosystem services and well-being
(MA2005)
2006/5/22
13
14Ecosystem Services and Natural Capital
- Goods (Resource of Agriculture etc.)
- Ecosystem services (Air, Water)
- Amenity, and intrinsic values are estimated to be
in US16-54 trillion per year, most of which is
outside the market
15Overview
- Requiem to MS Yield theory
- Adaptive management is useful for uncertain,
dynamic stocks, but - Yield is a small part of ecosystem services
- MS Ecosystem Services is more prudent and enhance
biodiversity - To ecosystem comanagement
- Comprehensive indicator of biodiversity
16Ecosystem services V(N, C)
- 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 biomass
2008/3/2
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17Regulating services S(N) S?N2/(B2N2)
(S?, B) (100,10)
(S?, B) (50,50)
2008/3/2
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18Mathematics
- Stock dynamics dN/dt (r aN)N C,
- Catch and yield C qEN, Y(C) pqEN,
- Regulating service S(N) S?N2/(B2N2),
- 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
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19Maximum Sustainable Ecosystem Service
(S?, B) (100,10)
(S?, B) (50,50)
(S?, B) (0,-)
2008/3/2
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20MSY vs MSES with process uncertainties
MSY
MSES
year
21MSES 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) Si?Ni2/(Bi2Ni2)
- We obtained EMSES ? Y(E) and EMSY ?V(E)
2008/3/2
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(a)
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2008/3/2
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23Resultant 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
24MSES saves fishing efforts
Ban-on-Fishing
2008/3/2
24
25Overview
- Requiem to MS Yield theory
- Adaptive management is useful for uncertain,
dynamic stocks, but - Yield is a small part of ecosystem services
- MS Ecosystem Services is more prudent and enhance
biodiversity - To ecosystem comanagement
- Comprehensive indicator of biodiversity
2612 Principles of Ecosystem Approach of CBD
- The objectives are a matter of societal choice.
- Management should be decentralized to the lowest
level. - ... managers should consider adjacent
ecosystems. - usually manage in an economic context.
- Any such ecosystem-management programme should
- Conservation of ecosystem structure and
functioning should be a priority target of the
ecosystem approach. - Ecosystem managed within the limits of their
functioning. - undertaken at the appropriate spatial and
temporal scales. - Recognizing the varying temporal scales and
lag-effects, objectives should be set for the
long term. - Management must recognize the change is
inevitable. - The ecosystem approach should seek the
appropriate balance between conservation and use
of biological diversity. - should consider all, including scientific and
indigenous and local knowledge, innovations and
practices. - involve all relevant sectors of society and
disciplines.
27Fishers 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.
28Coastal Foodweb at Shiretoko Heritage
Most of keystone species are caught and recorded
by local fishers org.s! Sustainable fisheries
play roles of umbrella species like top
predators!
28
Draft food web by SC
29Fisheries catch statistics in Shiretoko Area
Very informative time-series data for monitoring
the changes in ecosystem structure/functions
tons
29
Made by Mitsutaku Makino
30Reality 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-effici
ent fisheries are rational for enjoying fishery
rent, but not always so in sustaining total
ecosystem services for society.
31Fishers 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).
32Voluntary Activities (1)
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/amhiranaigy
okyo/)
33R1 Voluntary regulation of walleye pollock
- 177 boats fished walleye pollock in 1995
- Decreased to 86 boats in 2004 (49 reduction)
- Compensation to retired fishers by Fisheries
Organization - Fishing ban during Mar 20-end since 1995
- Fishing ban area expanded in 2005
Since 1995
33
Bottom trawling is totally prohibited in the
coastal area
34Role 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.
35From fisheries comanagement to ecosystem
comanagement
- Fisheries comanagement will not always lead to
the ecosystem management - It is likely that VMSES gt VMSY and EMSES lt 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).
36Overview
- Requiem to MS Yield theory
- Adaptive management is useful for uncertain,
dynamic stocks, but - Yield is a small part of ecosystem services
- MS Ecosystem Services is more prudent and enhance
biodiversity - To ecosystem comanagement
- Comprehensive indicator of biodiversity
37Convention 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
38Draft framework of marine biodiversity by Matsuda
Driving forces/Pressures
State/Impacts
Response
- DP1Fisheries exploitation
- Overfishing
- By-catach
- Aquaculture
- Bottom trawling
- Catch of marine mammals
- SI1 Loss of species richness
- Mean trophic levels
- Fish stock biomass
- Mammals, birds turtles
- R1 Sustainable use
- Catch regulation
- Ecolabels
- Stock rehabilitation program
- DP2 Civil engineering
- Fluvial sediment
- Reclamation, artificial shore and breakwater
- Gravel dipping
- SI2 Habitat loss/degradation
- Sand beach
- Sea grass/weed beds
- Tidal flat
- Coral reefs
- R2 MPAs by
- International MPAs
- National parks
- Voluntary MPAs
- Nature restoration projects
- DP3 Pollution and debris
- Eutrophication
- Oil spilling
- Exotic species
- Chemicals (TBT)
- SI3 Material cycling
- Red tide, blue tide
- Imposex of snails
- R3 Env. regulations
- Env. Impact Assess.
- BOD emissions
- TBT regulation
- SI4 Genetic pollution
- Salmonids
- DP4 Climate change
- Global warming
- pH decrease
39DP3 Exotic marine species
40DP3 PCDDs, PCDFs and Co-PCBs in Tokyo Bay
Sources and Contribution,
41SI1 Fishing down (MA 2005)
- In Japan??? F-MAPs mission?
42SI1 Catch and mean trophic levels in Japan
Fishing ground changed decadally.
43SI1 trend in catch and stock of Red Sea Bream
and Japanese sardine
http//abchan.job.affrc.go.jp/digests20/index.html
Stock (1000 tons)
Harvest rate
Stock (1000 tons)
Harvest rate
Stock (1000 tons)
Harvest rate
Harvest rate
Stock (1000 tons)
Red Sea Bream (West Sea of Japan/Southeast China
Sea)
Japanese sardine (Pacific stock) Japanese sardine
(total)
Catch Catch of wild larvae Seed release
ABC TAC Catch
No. indivuduals (10,000)
Caatch (1000 tons)
44SI2 Reduction of sea grass/weed bed in Seto
Inland Sea
45SI2 Trend and volume of suspended load
?????
www.nilim.go.jp/lab/dbg/pdf/200806_fac.pdf
105 m3
gt1m increase
104 m3
gt1m decrease
103 m3
46SI3 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)
Babylonia japonica
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.
47R1 Voluntary regulation of walleye pollock
- 177 boats fished walleye pollock in 1995
- Decreased to 86 boats in 2004 (49 reduction)
- Compensation to retired fishers by Fisheries
Organization - Fishing ban during Mar 20-end since 1995
- Fishing ban area expanded in 2005
Since 1995
47
Bottom trawling is totally prohibited in the
coastal area
48R1 The number of registered MSCs in the World
and Japan
World Japan
49R2 MPA Construction to protect spawning/breeding
area (by public expenses)
?????
(Sited from Kyoto Institute of Oceanic and
Fishery Science HP)
50R2Sandfish fishery mgmt at Akita Pref.
Arctoscopus japonicus Mgmt actors Local
fishermen, Local research station, etc.
- 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
www.pref.akita.jp
Catch (tons)
Mapmap Ver.6.0
51Conclusion
- 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.
2008/3/2
51
52Abstract
- 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 gtgt 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.
53Overview
- Requiem to MS Yield theory
- Adaptive management is useful for uncertain,
dynamic stocks, but - Yield is a small part of ecosystem services
- MS Ecosystem Services is more prudent and enhance
biodiversity - To ecosystem comanagement
- Comprehensive indicator of biodiversity
54Overview
- Requiem to MS Yield theory
- Adaptive management is useful for uncertain,
dynamic stocks, but - Yield is a small part of ecosystem services
- MS Ecosystem Services is more prudent and enhance
biodiversity - To ecosystem comanagement
- Comprehensive indicator of biodiversity
55Regulating services S(N) S?N2/(B2N2)
Maximum Sustainable Yield
(S?, B) (100,10)
(S?, B) (50,50)
Unsustainable Fisheries
No take zone
2008/3/2
55