Transcript Slide 1

Implementing EBFM in the (NE)
U.S. Atlantic
Jason Link
NEFSC
Woods Hole, MA
EBFM


Moving beyond when, why and what
Now we’re to HOW?
One Main Theme of EBFM:
CONFRONTING TRADEOFFS
“The aim of an argument or discussion
should not be victory, but progress."
- Joseph Joubert
Heurism

Understanding Ecosystem Functioning

Relative Importance of Different
Processes

Advancing Scientific Theory
Tactical Management

Revised Stock Assessments


Yield Adjustments
Altered Biological Reference Points, etc.

Direct Impacts on Target, Non-Target
Species, PETS, Habitat, Agg Groups

Specific “What If” Scenarios and
Gaming

BINDING IN SCOPE
Strategic Management

Assessing Biomass Tradeoffs

System Level Emergent Properties

Evaluating Alternate Stable States

Evaluating Long Term Recruitment
Bottlenecks

General “What If” Scenarios and
Gaming, Long Term Trends

BOUNDING IN SCOPE
Gradient of Possibilities
Stock/Single
Species
Multi-species
Aggregate
Biomass
Ecosystem
Gadids
Flatfish
Pelagics
SS models, forget
ecosystem issues
Multi-species
SS assessments assessments
with explicit M2
or habitat or
climate
considerations
Multiple SS
assessments
in “harmony”
Aggregate
Biomass
Models
Messy
Picture
Here
Whole System
Models, forget
pop dy
"I am always doing that which I can not do,
in order that I may learn how to do it."
-Pablo Picasso
SS Add-ons




Increasing #s of extant
cases incorporated into
assessments
Still slow “uptake kinetics”
in overall Mgt process
Yields generally lower if
predation is considered as
a component of total
mortality
Remains critical for most
“forage” species
Starting to include
environmental cues
250
Standard Assessment
Catch (000's mt)

200
150
Predation Included
100
50
0
2000
2002
2004
2006
Year
2008
2010
e.g., Atlantic Herring M2 and F during 1959-2002
1.4
Mortality Rate
1.2
1.0
0.8
0.6
0.4
0.2
0.0
1959 1964 1969 1974 1979 1984 1989 1994 1999
Year
M2
F
e.g., Pandalid Shrimp Assessment
300
Biomass
B.25
250
B.50
B.60
200
Pandalus borealis consumed
150
100
50
0
1980
1985
1990
1995
2000
2005
2010
e.g., Menhaden: Estimated Abundance With and W/out Predation
9000
Numbers (millions)
8000
Age 1
7000
6000
5000
4000
3000
2000
1000
Predators
0
1982 1983 1984 1985 1986 1987 1988 1989 1990 1991 1992 1993 1994 1995 1996
Numbers (millions)
3500
3000
Age 2
2500
2000
1500
1000
500
0
1982 1983 1984 1985 1986 1987 1988 1989 1990 1991 1992 1993 1994 1995 1996 1997
No Predators
e.g., Loligo Production+M2 Model
1.6
B/BMSY
No Predation
With Predation
1.4
Relative Biomass
1.2
1
0.8
0.6
0.4
0.2
0
1987 1988 1989 1990 1991 1992 1993 1994 1995 1996 1997 1998 1999 2000 2001 2002
Year
e.g., Linked Climate-Population Models
Climate (IPCC Air Temperature to
Estuarine Temperature)
Fisheries (Environmentallyexplicit population model: R as a
function of T)
F=0.8
550 ppm
Management (Link Forecasted
SSB to Management
Benchmarks)
Based on mechanistic hypothesis developed
in Hare and Able (2007) Fish Oceanogr 16:
31-45.
Multispecies Models


MSVPA, MSProd, AggProd etc.
Effects of predation the main emphasis
e.g., MSVPA




>15 spp
Age/size structured
Focuses on M2 of
main “forage” stocks
Formal review
process for 1 region,
2nd planned
B.
1.6
1.4
MSVPA M1
MSVPA M2 ages 0-1
Mortality rate
1.2
1
0.8
0.6
0.4
0.2
8
19 3
84
19
8
19 5
86
19
87
19
88
19
89
19
90
19
91
19
92
19
9
19 3
94
19
9
19 5
96
19
9
19 7
98
19
99
20
00
20
01
20
02
19
19
82
0
Temporal variability in predation mortality on young age classes of Atlantic mackerel
e.g., MS Production & Aggregate
Production Models


Used as part of recent GARM
Basically same as SS, just for groups of
stocks




Simulators
Fitting
Context
Scenarios
Base Scenario
250
Guild Biomass- Base Scenario
200
150
100
50
0
0
2
4
6
8
10
12
14
16
18
20
22
24
26
28
30
Time
Benthivores Planktivores Shrimp-Amphipods Shrimp-Fish Piscivores
Scenario 3: Over-Fish Pelagics
250
Guild Biomass- Scenario 3
200
150
100
50
0
0
2
4
6
8
10
12
14
16
18
20
22
24
26
28
30
Time
Benthivores Planktivores Shrimp-Amphipods Shrimp-Fish Piscivores
Aggregate Production Model
120
Predicted Biomass
Survey
1500
100
80
60
1000
40
500
20
0
1960
0
1970
1980
Year
1990
2000
Survey Index (kg/tow)
Predicted Biomass (kt)
2000
EMAX


Energy Budgets/ Network
Analyses
Emerging as a tool for:







Heurism
Strategic Mgt
Tradeoff Evaluation
MSE
Pelagic
Fisheries
Sea
birds
Considered as part of formal
trade-off analysis
Dynamic models next
Used as part of recent
GARM
Micronekton
Small Copepods
Discards
Pelagic
Sharks
Baleen
whales
Medium
Pelagics
Small Pelagics
Anadromous
Demersal
Fisheries
Odontocetes
Demersals
Piscivores
Demersals
Omnivores
Demersals
Benthivores
Small Pelagics
Squid
Coastal
Sharks
Pinnipeds
HMS
Larval & Juv. Fish
Small Pelagics
Other
Small Pelagics
Commercial
Mesopelagics
MegaBenthos
Other
Shrimp et al.
MegaBenthos
Filterers
Large Copepods
Microzooplankton
Gelatinous ZP
Primary Producers
MacroBenthos
Molluscs
Bacteria
MacroBenthos
Crustaceans
MacroBenthos
Polychaetes
MacroBenthos
Other
Detritus-POC
DOC
Cumulative Biomass (g m-2)
250
200
150
GOM
100
GB
SNE
MAB
50
0
1
2
3
Trophic Level
4
5
GOM Aggregated System Flow
ECOGOMAGG
X11
X6
X2
X12
X4
X7
X1
X13
X8
X5
X14
X3
X9
• A home grown dynamic
model
• Builds off of EMAX
(energy budget) outputs
X10
X15
X16
X1 Phytoplankton
X2 Bacteria
X3 Zooplankton
X4 Gelatineous zoop
X5 Microneckton
X6 Macro-benthos
X7 Mega-benthos
X8 Shrimp
X9 Pelagic fish
X10 Demerdal fish
X11 Sharks
X12 HMS
X13 Pinnipeds
X14 Baleen whales
X15 Toothed whales
X16 Seabirds
ATLANTIS NEUS



Full blown ecosystem
simulations
Still in validation &
verification stage
An important Mgt tool



Systemic Perspective
Virtual “perturbations”
MSE catch all model
Northeast United States – (22, 8)
0 Pelagic
50
120+
300+
Epibenthic
Sediment
Squids, No Fishing, yr 0 (1964)
Squids, No Fishing, yr 46
Ecological Indicators
• Outputs both from empirical and modeling studies
• Evaluate a broad suite of ecosystem properties
• Vetting ongoing, MV Approaches
• Translation to Decision Criteria is key, ongoing (EO-F)
• Remains to be incorporated into Mgt Process
2
1995
1.5
1973
1977
1
-1.5
PC 2
198
5
0
-1
198
0
-0.5
-0.5
Bpisc
0
-1
0.5
1
198
9
1.5
2
120
Mean kg Tow-1
0.5
196
8
-2
Decision Criteria:
Aggregate Biomass
1999
100
< Bbenth + Bplank
OK
Piscivores
Benthivores & Planktivores
80
N/A Threshold
60
40
20
-1.5
-2
PC 1
0
1963 1968 1973 1978 1983 1988 1993 1998 2003
> Bbenth + Bplank
Limit
Summary of NEUS Model e.g.s


Several modeling efforts at various stages
along the modeling gradient
Working at both ends of the gradient to make
ecosystem-based mgt advice operational






Several research/development activities
A few instances of review in SAW/SARC/TRAC/GARM
and like processes
Most instances as ESAMs/MRMs;
Systemic outputs still being developed
Not as data limited as elsewhere, but have
identified clear data gaps
Tool and software development continually
ongoing
“Not only was an ecosystem management
approach legal, it was mandatory if all
applicable laws were to be simultaneously
obeyed.”
- Jack Ward Thomas
MSE/MPs, IEAs
Observations
Monitoring or
Surveys
Ecosystem
IEA
Models
Implementation
Decision Rule
MSE, virtual world for mgt institutions
Education and Outreach
Ecosystem Status Report
For the Northeast U.S. Continental Shelf Large Marine Ecosystem
Ecosystem Assessment Program
Northeast Fisheries Science Center
April, 2009
Main Findings
The Northeast U.S. continental shelf large marine ecosystem has undergone sustained
perturbations due to environmental and anthropogenic impacts over the last four
decades, resulting in fundamental changes in system structure.
Thermal conditions of the ecosystem are changing, the result of the warming of coastal and
shelf waters and cooling in the northern end of the range. As a consequence, there has
been a constriction of thermal habitats in the ecosystem, poleward shifts in distributions
some of fish species and changes to a warmer-water fish community.
Zooplankton community structure has changed in concert with climate and physical
processes acting over the North Atlantic Basin indicating the importance of remote
forcing to the function and structure of the ecosystem
The direct and indirect effects of species-selective harvesting patterns have also contributed to
shifts fish community composition which is now dominated by small pelagic fishes and
elasmobranch species (skates and small sharks) of relative low economic value,
The trajectory of regional human population size suggests that anthropogenic pressure in the
ecosystem will continue to increase.
The Northeast U.S. Continental Shelf is classified as overfished from an ecosystem perspective
according to established criteria for this designation.
Contents:
1 Introduction
2 Climate Forcing
3 Physical Pressures
4 Primary and Secondary Production
5 Upper Trophic Level Dynamics
6 Anthropogenic Impacts
7 Integrative Ecosystem Measures
Summary
Literature Cited
Further Information
Acknowledgments
Glossary
1
2
4
11
19
22
25
28
29
30
30
31
water and domestic fishing fleets [3]. Further, the
region has experienced changes in climate and
physical forcing that have contributed to large-scale
Figure 1.1 Map of study region on the Northeast continental
shelf of the United States.
1 Introduction
The Northeast U.S. Continental Shelf Large Marine
Ecosystem (NESLME) is a dynamic, highly
productive, and intensively studied system providing
a broad spectrum of ecosystem goods and services [1,
2]. This region, encompassing the shelf area between
Cape Hatteras and the Gulf of Maine (Figure 1.1),
spans approximately 250,000 km2 and supports some
of the most lucrative fisheries in the nation. The
system has also historically undergone profound
changes as a result of heavy exploitation by distant-
alteration in ecosystem structure and function.
Projections of future climate change highlight the
need to understand the effects of natural and
anthropogenically driven perturbations to this system
Stakeholder Interactions leading to
Implementation

Numerous presentations at MAFMC, NEFMC




MREP
Numerous mtgs with NGOs, Industry Groups



SSC, Ecosystem Cmtes beginning to uptake
FEPs
Surveys, Workshops, Discussion Groups, Cooperative
Research, Collaboration, etc.
NERO Collaborations and Working Groups
Academic Partners

Buy in & Collaboration
Ecosystem Assessment Program




Started < 1 year ago
Established to integrate all of NEFSCs efforts
Goals are to develop LMR management products
from an EBFM perspective, and to facilitate
interdisciplinary endeavors within our Center and
region
The one part of the organization dedicated
primarily with the task of taking a systemic,
holistic, integrated view of our ecosystems
The Key for Any Renewable
Resource Management
Rate of Removal of a resource
<=
Rate of Replenishment of that
resource
"When there is a hill to climb, don't think
that waiting will make it smaller."
-George Bernard Shaw
Plans/Suggestions for Implementation:
Technical





Predation mortality (M2) should be included
in stock assessments of forage (common &
commerical prey) species (e.g., fish &
invertebrates)
Explore environmental drivers on r, g, dist,
etc. for major stocks
Tradeoffs among species, fleets, and sectors
needs to be modeled explicitly
Continue with multiple modeling efforts
Venues & fora for model review and output
dissemination need to be revisited
Plans/Suggestions for Implementation:
Institutional/Organizational





Adoption of an MSE framework to evaluate
scenarios and tradeoffs
Develop integrated products (EAR, ESR, IEAs,
etc.)
Continue outreach and stakeholder
engagement/involvement
Work within existing institutional processes
(e.g., SARC/TRAC/etc., SSC, Ecosystem
Cmtes, ROs) to provide both modified SS and
Systemic Mgt Advice
“Keep it simple, keep it safe” – sensu Gandalf
If you think you can or think you can’t,
you’re right.
- Henry Ford
EBFM is as easy as pie
Extra Slides in my hip pocket
e.g.- Atlantic Herring










Highly migratory, locally dominant, spatially
overlapping with many species
Predation by protected species, commercially valuable
species- odontocetes, seals, birds, fish, invertebrates
Competition with protected or commercial speciesplanktivores, ichthyoplanktivores
Predation on larvae of commercial species
Large fishery potential
Lower trophic levels
Very high trophic efficiency
Horizontal flux, high biomass
High linkage density
Temperature mediated changes in distribution,
migration or production?!