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Living Marine Resources Cooperative

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Title: Living Marine Resources Cooperative


1
The Foundation of Science in Marine Resource
Management and Policy
Michael J. Fogarty NOAA/NMFS/NEFSC
Marine Fisheries Policy Seminar Series
Living Marine Resources Cooperative
Science Center (LMRCSC)
2
Topics to be Covered
  • Basic Concepts of Population Biology
  • The Concept of Biological Production
  • Growth
  • Maturation
  • Mortality
  • Recruitment
  • Management Strategies and Reference Points
  • Control Rules
  • Translation and Transmission of Scientific Advice
  • Towards Ecosystem Approaches to Fishery Management

3
Population Biology Depends on The Development
and Use of Mathematical Models
4
You are Used to Seeing Many of the Concepts
ofPopulation Biology in Humans
5
  • Exponential Growth
  • Populations increase proportional to their
    biomass (the rate of change is a function of
    stock size).
  • Thomas Malthus (1798) used the exponential growth
    model to project the human population explosion.
  • Currently used to model bacterial populations.

6
  • US Population 1790-2000

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10

So What Information do we Need?
  • Basic Biology
  • lifespan
  • growth
  • maturity rate
  • movements
  • Fishery Information
  • Historical development (areas, gears)
  • Past and current regulations (size limits, gear
    restrictions).
  • Catch (landings, discards, age/size distribution)
  • Effort (catch rates)
  • Surveys
  • Distribution
  • Relative abundance and biomass over time
  • Age/size structure
  • Life history (growth, maturity)

11

Where do we get the Numbers? NEFSC Monitoring
and Observing Program Elements
  • Satellite Oceanography
  • Oceanographic Buoys/Moorings
  • Standardized Research Vessel
  • Surveys
  • Ships of Opportunity CPR Program
  • Observer Program
  • Logbooks
  • Cooperative Industry Research

12
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13
Population Dynamics
  • Age Structure
  • Reproductive Biology
  • Growth
  • Mortality
  • Recruitment

14
The Basic Fish Population Model
dP (G R) (M C)
dP change in population biomass G growth R
recruitment M natural mortality C catch
15
Some Definitions
A population is a group of interbreeding
individuals of a species in a particular area
A stock is specified management unit, possibly
corresponding to population but not necessarily so
16
Unit Stock
Functions as a management unit
Gulf of Maine Cod Stock
Isolated reproductively
Different growth, spawning areas, maturation
Georges Bank Cod Stock
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18
Change in Biomass Increases due to Recruitment
Increases due to Individual Growth
- Losses due to Natural
Mortality
- Losses due
to Harvesting
19
All these problems require some type of approach
to estimate quantities that are not easily
observed!
  • We cannot do a census of everything.
  • Its too expensive and also unnecessary!

20
Why is fish population dynamics important?
  • with population dynamics and models we can
    estimate something we cannot see the number and
    biomass of fish in the sea

21
Models of Individual Growth
22
Aging Fish
23
Atlantic Cod
24
How do we age fish?
Use microscope to count annual growth rings
25
How long do marine fish live?
  • Most in our region live 10-15 years
  • Redfish live 25-40 years
  • Sand eels live 3-5 years
  • Squids live about 1 year

26
Age Structure of Fish Populations
27
Why do we age fish?
  • If you know how many fish were alive at the
    beginning of the year at each age and how many
    have died during the year!
  • Then you can estimate fishing rates, biomass
    etc.
  • If you know how many new recruits are produced,
    you can predict future catch and biomass.
  • We can produce more detailed stock assessments
    and provide better advice.

28
  • Important points about age structure

Few Ages
Georges Bank Haddock under 2 different fishing
regimes
Heavily fished Lightly Fished
Many Ages
29
Growth
30
Why is Growth Important?
  • The weight gain in fish over time replaces
    biomass removed by fishing!
  • Understand the seasonality of the process
  • Essential for estimating biomass in the sea

31
Why Study Fish Growth?
  • We need to know how much fish weigh.
  • To estimate the weight of the catch
  • To estimate the biomass of fish in the sea

32
How do we get fish weights?
  • Weigh fish at the port when they are landed
  • Weigh fish at sea on commercial or survey vessels
  • Estimate the weight from length

33
Weight is a cubic function of length wtaL3
A 40 cm YT weighs .511 kg
We can convert length to weight easily
  • A 40 cm fish weighs .511 kg

34
  • We can use curves to describe the growth of fish
    in length and weight
  • These relationships fit well and are very useful

35
Fish Growth Facts
  • Fish Growth is Indeterminate
  • Fish grow fast when they are young
  • Growth slows with age, but never stops
  • Related to food, density, temperature

36
Reproductive Biology
37
What do we use maturity information for?
  • To calculate length and age at first spawning
  • To estimate peak spawning times and areas
  • To calculate spawner biomass

38
Maturation varies by species and region
Maturation is also sensitive to density,
temperature, food resources.
39
Mortality
40
Mortality Models
41
What is it?
  • Study of the loss of fish by natural and fishing
    related causes.
  • Estimating the rate of decline or the number of
    fish that die during some time period, usually 1
    year.

42
Why are mortality rates so important?
  • With them
  • We can determine the historical size of a stock!
  • We can estimate current biomass!
  • We can estimate next years biomass!
  • We can determine maximum sustainable yields!

43
There are many examples of exponential rates that
affect our daily lives!
  • The mortgage rate on your house!
  • The interest on your 401K retirement plan!
  • The life insurance premium you pay to your
    insurance agent!
  • Radioactive decay of spent fuel from a nuclear
    power plant!

44
An Example of exponential rates Compound
interest on a bank account!
Problem Calculate the size of your bank account
in 13 years with a 5 interest rate if you start
with 1000 dollars now!
You could multiply 1000 X 1.05 for the first
year and 1050 x 1.05 for the second year, and
. For 13 years 1885.65 or you can find the
exponential interest rate and do it the easy way
Iln 1.05.04879 Total 0
x eI x t
Total 1000 x e 0.0487913 1000 x
exp(.04879 x 13) 1885.65
45
Mortality Rates for Fish Are Very Much the Same!
  • Mortality is a decay process!

Instead of being positive like an interest rate,
it is negative since fish are dying from fishing
or natural causes
46
  • Total Instantaneous Mortality Z
  • How do we calculate this quantity?
  • SNt/N0
  • Z-ln(S)
  • Then S Nt/N0
  • 736/1000
  • .736
  • and Z-ln(S)
  • -ln(.736)
  • .306

So if you know how many fish were alive at the
beginning of the year, say 1000 and how many are
left at the end of the year, say 736
47
  • Fishing Mortality Rate
  • ZFM
  • From Previous page Z.306
  • and for most groundfish and flats with M.2
  • ZFM
  • .306F.2 ,
  • .306-.2F
  • F.106

48
Effects of Different Fishing Rates
49

Total Exponential and Annual Mortality Rates
Z
A
These are the equivalent percentage rates
These are total exponential mortality rates
In science jargon we refer to these as
instantaneous rates
  • A 1-e-Z
  • SNt1/Nt
  • Z-lnS

50

Mortality Rates Relating the two Types
  • Important Points
  • Annual Rates are Percentage Rates
  • Instantaneous Rates are Exponential Rates
  • A Z of 3 an A of 95
  • Instantaneous rates are handy because they can be
    added, subtracted, multiplied etc
  • Z F M
  • Annual rates cannot be manipulated this way

51
More on Getting the NumbersVirtual Population
AnalysisSimultaneous Estimation of Fishing
Mortality and Population Size
52

Virtual Population Analysis
  • Over the lifespan of the 1987 yearclass, 77
    million fish were caught.
  • We also know that some fish died from natural
    mortality.
  • So, at a minimum, there were 77 million fish when
    they were 1 year olds.
  • But this is just the population we saw (the
    virtual population) from the underlying true
    population.
  • VPA reconstructs the true population from the
    virtual population.

53

VPA
  • Reconstruction of all yearclasses gives a total
    population estimate.
  • Input Data
  • catch at age
  • estimate of natural mortality
  • initial guess about abundance of survivors at the
    oldest age.

54

VPA Calibration
  • Initial guesses are replaced with estimates
  • oldest age of historical yearclasses estimated by
    assuming that age-7 fish have the same
    vulnerability to the fishery as ages 4-6
  • CFxN
  • C/FN
  • yearclasses that are alive now require more
    information.
  • need an independent index of relative abundance
    over time.

55

VPA Estimates
  • Informative Assessment
  • Example SNE yellowtail
  • Estimates of stock size and F,
  • But also age distribution, recruitment, mature
    biomass, etc.

56
Recruitment
57
Stock-Recruitment Models
58
What is it?
  • New fish entering the population from a previous
    years spawning.

59
Why is Recruitment Important?
  • It is the engine that drives a fishery
  • Provides the new fish that sustains the catch in
    the future!
  • If we can estimate it we can predict future stock
    status.
  • It changes annually based on spawner biomass and
    environmental factors.

60
Fluke Recruitment-age 1
  • New fish entering the population from a previous
    years spawning
  • Different each year, related to spawning stock
    size and environmental factors

61
Why is it important to know how much spawning
stock there is?
  • Spawning biomass is the equivalent of a fishery
    bank account
  • It produces the interest (recruits) for the
    following years.
  • Based on current knowledge, more is better!

62
Stock-Recruitment
63
Why is the Study of Stock-Recruitment So Important
  • Used to forecast stock status
  • Understand level of spawning biomass necessary to
    produce large sustainable catches
  • Calculate key values (reference points) for the
    stock

64
Stock-Recruitment Data
Use the data or Fit a curve and use the curve and
its properties.
65
Biological Reference Points
66
What are Biological Reference Points
  • Key fishing rates or biomass levels that are
    related to the maximum potential of a stock
  • A fishing rate (F) that produce the highest
    catches or spawning potential
  • A biomass level that produces the highest catches
  • Produced from relatively simple models
  • Yield per recruit, surplus production, SR

67
Limit and Target Reference Points
68
Target
Management targets are
  • A level of F that gets you to a goal.
  • An F target gets you to a desired place!
  • A level of biomass that is a goal.
  • A biomass target is a desired place!

69
Limits
Limits are
  • Fs you shouldnt exceed, a biomass you shouldnt
    go below
  • A key reference point value like Fmsy or Bmsy

70
What is overfishing?
  • Catching too many fish
  • Applying a fishing rate that is too high.
  • Result
  • The stock cannot produce enough recruits to
    maintain itself at a productive level.

71
Why does it matter?
  • Causes the stock to decline to a less productive
    state
  • Reduces future catches and dollars earned
  • Removes fish too early in their life
  • Reduces recruitment, in many cases dramatically
  • Not sustainable

72
Types of Overfishing
  • Growth overfishing- related to the size and age
    of fish
  • Recruitment overfishing- related to the
    production of new recruits

73
Growth Overfishing
  • Removing too many young fish
  • Size of fish is too small relative to their
    potential

74
Examples of Growth Overfishing
  • Scallops- were harvested at small sizes for
    decades. Potential was shown when scallops that
    were 4x larger were encountered in closed areas
  • Grey sole- discards were very large before the
    nordmore grate was used in the shrimp fishery and
    larger mesh in the groundfish fishery.

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76
Recruitment Overfishing
  • Rate of fishing that reduces stock size to the
    point where recruitment is impaired.
  • Removing too many fish so that there are
    insufficient recruits to keep the stock at a
    productive level

77
Landings from the Georges Bank haddock fishery
1904-2001
Stock collapsed by the late 1960s
Sustained catch at 45,000 mt
Cost of overfishing over 1 million mt of yield
foregone during 1970-2001
78
Surplus Production Models
Production Function
79

Populations Cannot Grow Without Limits
  • Limited Population Growth
  • Logistic growth populations increase
    proportional to their biomass, but the rate of
    increase slows as the population approaches its
    carrying capacity.
  • Rate of change (production) is maximum when the
    population is at half of its carrying capacity.

80

Production Models
  • Grahams Theory of Sustainable Fishing (1935)
  • If removals can be replaced by stock production
    each year, the fishery is sustainable.
  • If stock size is maintained at half its carrying
    capacity, the population growth rate is fastest,
    and sustainable yield is greatest (Maximum
    Sustainable Yield).

81
  • Production Models
  • Stock Status
  • Recent models can use observed yield and multiple
    stock size indices to estimate F and B by
    smoothing and scaling.
  • Smoothing stock size estimates are fit to survey
    data using the simple population process
  • logistic growth and observed catch.
  • More informative than 3-year average.
  • Scaling

82

Production Models
  • Stock Status
  • Scaling survey observations are scaled to
    absolute biomass estimates by evaluating the
    response in survey data to absolute removals.
  • When catch was not sustainable, stock decreased
    (1970s-1980s).
  • When catch was less than potential production,
    stock increased (1960s, 1990s).

83
Fit a simple model,estimate parameters, produce
a symetric yield curve (Shaefer), and you get
MSY
Bmsy

84
Other Important Reference Points
  • Fmax- fishing rate that produces maximum yield
    per recruit
  • F0.1- fishing rate that is 1/10 of the slope of
    the Y/R curve at the origin
  • F40- fishing rate that gives 40 of the maximum
    spawning potential

85
Yield and Spawning Biomass Per Recruit Models
86
F0.1
Fmax
87
F40
88
Biomass Limit
Think of Bmsy as a minimum amount
You dont want to drop below this amount
Bmsy
89
F and Biomass Targets
If you fish at Fmsy or below (target) youll get
to Bmsy (target)
Bmsy
90
How Do We Prevent Overfishing?
  • Limit the number of fish removed!
  • Indirect Measures like mesh sizes, area closures,
    time closures, minimum fish sizes.
  • Direct Measures like effort limitation, catch
    quotas, individual quotas.

91
Control Rules
92
What is a Control Rule?
  • A roadmap to a goal (higher stock size)!
  • Shows you how to get from an undesirable place
    (overfished) to a better place!
  • Can be a definition, a graph, or a mathematical
    expression.

93
Control Rule
In the context of SFA
Fishing rate limit is Fmsy
Biomass limit is ½ Bmsy
94
When is Overfishing Occurring Using Current
Guidelines?
95
Overfishing, F too high
96
Georges Bank Haddock 1930-1999
Georges Bank Haddock a Long History of overfishing
Overfishing was occurring in every year except
during 1995-1999
We have done real well since 1995!
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99
When is a Stock Overfished Using Current SFA
Guidlines?
100
Overfished, biomass too low, below ½ Bmsy
101
Georges Bank Yellowtail Flounder
Overfishing occurred for almost entire history
Biomass was overfished for entire history
Now, low F, recovered biomass, good job!
Dramatic response in recruitment
102
Stock Assessment Review Committee (SARC)
103
What is the SARC?
  • Peer review process to review assessments and
    give advice!
  • Review several stock assessments from working
    groups.
  • Write an advisory document for the NEFMC and MAFMC

104
Assessment Review
  • Determine if the fishing rate is too high
  • Determine if the biomass is too low.
  • Project future biomass under several different
    assumptions

105
SARC Products
  • Assessment Document
  • Advisory Report
  • Forecast Stock Status 2 years or more ahead

106
Advice
  • Suggested actions for controlling or not
    controlling catch.

107
SARC What is the point?
  • To serve as the interface between scientists and
    managers
  • To determine the current status of fish stocks
  • To distill stock assessments into a roadmap for
    managers to change or not change current
    conditions.

108
The SARC Process
109

Closing Thoughts Moving Toward Ecosystem
Approaches to Fisheries
Management
110

Single Species Dynamics Reference Points
111

Effects of an Environmental Shift
Favorable Environment
Unfavorable Environment
If Intrinsic rate of increase is affected
112
  • Multispecies Models Technical Interactions

113
  • Multispecies Models Technical Interactions

114

Multispecies Fisheries Biological Interactions
Prey Yield
Prey Fishing Mortality
Predator Fishing Mortality
115

Fishing Effects on Carrying Capacity
Standard Model
Habitat Effects Model
116

117

118
The Challenges Ahead
  • Develop Strategies for Consultation with
    Stakeholders
  • Choose Specific Management Objectives with
    Stakeholder Input
  • Develop Indicators of Ecosystem Status
  • Develop Predictive Models of Ecosystem Dynamics
  • Develop Precautionary Management Strategies to
    Meet Chosen Objectives
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