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Modeling fisheries and stocks spatially for Pacific Northwest Chinook salmon Rishi Sharma, CRITFC...
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Transcript of Modeling fisheries and stocks spatially for Pacific Northwest Chinook salmon Rishi Sharma, CRITFC...
Modeling fisheries and Modeling fisheries and stocks spatially for stocks spatially for Pacific Northwest Pacific Northwest Chinook salmonChinook salmon
Rishi Sharma, CRITFCRishi Sharma, CRITFC
Henry Yuen, USFWSHenry Yuen, USFWS
Mark Maunder, IATTCMark Maunder, IATTC
Structure of TalkStructure of Talk
Background Background Life History and relationship to modelLife History and relationship to model Estimating catch in Fisheries by stock.Estimating catch in Fisheries by stock. Statistical Catch at Age Analysis (SCAA).Statistical Catch at Age Analysis (SCAA). Adapting to a multi-stock framework.Adapting to a multi-stock framework. Precision in Exploitation rates.Precision in Exploitation rates. Wrap Up.Wrap Up.
BackgroundBackground
•Jurisdiction.
•Fisheries.
•Value ($20-50 M/yr X-vessel price).
•Cost tagging and assessment ($15 M/yr).
Chinook Life CycleChinook Life Cycle
Eggs, Fry & Juveniles
NaturalSpawning
Escapement (Age 2, 3,4, 5,6)
Ocean (Age 2,3,4,5, 6)
Age 2 Ocean Recruits
Maturation (% 2, 3, 4, 5)
No
Yes
Nat Mortality
Freshwater
Ocean
Tag Data used in Tag Data used in assessmentassessment
Escapem
ent
# of fish
Life History (TIME)
Cohort AnalysisCohort Analysis
Pop
ulat
ion
Tot
al
Fishery
3
Fishery
4Fish
ery 1
Fishery
2
Natural Mortality
Catch
PopulationER =
Population
ERROR
Age 2 recruits
Estimate Age 2 recruits
Spawners
Ages 2,3,4,5
MaturationEstimated from tag data
Catch (ocean)
Ages 2,3,4,5
Catch
(fresh
water)
Ages 2,3,4,5
Natural Mortality
States of Nature (have a time dynamic)
CURRENT VPA MODEL MECHANISM
Projected
By Cohort analysis estimates from a Base Set of Years
CWT Based
Size limit adjustments
Projected
By Cohort analysis estimates from a BaseSet of Years
CWT Based
Size limit adjustments
Spawners
(Projected to equal Forecast & Observed Spawners over multiple ages, i.e. over the cohort)
Freshwater
Ocean
Age 2 recruits
Estimate Age 2 recruits
Spawners
Environmental Forcing functions
Ages 2,3,4,5
MaturationMaturation
estimated
Catch (ocean)
Ages 2,3,4,5
Catch
(fresh
water)
Ages 2,3,4,5
Natural Mortality
States of Nature (have a time dynamic)
SCAA MODEL MECHANISM
Catch (ocean)
Projected
Fn (abun, Vuln and Catchability, ocean)
Effort Known
Catch (f_water)
Projected
Fn (abun, Vuln and Catchability, Terminal)
Effort Known
Spawners
(Projected)
Fn
(TR-Term_Catch)
Trade-OffsTrade-Offs
Lesser assumptions.Lesser assumptions. Estimation framework.Estimation framework. Numerically intensive & Challenging.Numerically intensive & Challenging.
Essential ApproachEssential Approachta,timeage,timeage,1 time1,age MaturationDeathsNumberNumber
timeage,timeage,timeage, ityNat.MortalFishingDeaths
ttimeagetime Efforterabilityvutycatchabili *ln*rtalityFishing_Mo ,timeage,
n
f f
ftafta
f
fta
CCCL
12
2
,,,,
2,,2
)ˆ()exp
2
1)|(
n
f f
ftaftaffta
CCCL
12
2
,,,,,, 2
ˆlnlnln)|(ln
Maximum Likelihood Maximum Likelihood Estimation Estimation
Testing the ApproachTesting the Approach
Simulation TestingSimulation Testing
Used a Ricker stock recruit with process error. Used a Ricker stock recruit with process error. Simulated different catchability, vulnerability and Simulated different catchability, vulnerability and maturation schedules by different fisheries and maturation schedules by different fisheries and time periods.time periods.
Estimated the recruitment deviates, and thereby Estimated the recruitment deviates, and thereby age 2 recruitment.age 2 recruitment.
Estimated vulnerability, catchability and maturation Estimated vulnerability, catchability and maturation by time periods specified.by time periods specified.
Ran 10,000 times (each run takes approximately Ran 10,000 times (each run takes approximately 10 seconds-27 hours).10 seconds-27 hours).
Spawner to age 2 recruit curve
alpha
beta
Process Error
ε~N(0,σ2) F=qaEsaa
Ocean Catcha
Escapementa
OBS Error
SIMULATION MODEL
compare
Escapementa
Ocean Catcha
OBSERVATIONS WITH SIMULATED NOISE
Maturationaa
MODEL ESTIMATION
Terminal Catchaa
Age 2 Recruits
F=qaEsaa
Ocean Catcha
Terminal Catchaa
Escapementa
Terminal Catchaa
Escapementa
Maturationaa
Parameter Uncertainty25 year time series
Summary of simulationsSummary of simulations
Model has a high accuracy on estimating Model has a high accuracy on estimating Recruitment & Exploitation Rates.Recruitment & Exploitation Rates.
Model is biased (underestimating) on true Model is biased (underestimating) on true parameters on Catchability and Maturation.parameters on Catchability and Maturation.
The model does not appear to capture terminal The model does not appear to capture terminal vulnerability, though ocean vulnerability is vulnerability, though ocean vulnerability is marginally better. marginally better.
Adding measurement error to the data, creates Adding measurement error to the data, creates problems in estimation (lower error, CV<0.1, problems in estimation (lower error, CV<0.1, implies greater identifiability versus larger error, implies greater identifiability versus larger error, CV>0.1)CV>0.1)
4 Stock Model4 Stock Model
Spatial variation in stocks modeledSpatial variation in stocks modeled Spatial variation in fisheries modeledSpatial variation in fisheries modeled 2 Pool Model structure.2 Pool Model structure.
1. S.E. Alaska
2. WCVI
3. Terminal WCVI
4. Terminal Fraser
5. Terminal Queets
6. Terminal Columbia
1
32 4
5
6
Fisheries
URB
Lower FraserWCVI
Queets
4
1
4
12
,
2
,,,,
2
)ˆln()ln()ln()|((
i f if
ifif
ifif
CCCLLn
4 stock- 4 fishery model4 stock- 4 fishery model Parameters estimated:Parameters estimated:
– Recruitment deviate over time (25 years X 4 stocks)Recruitment deviate over time (25 years X 4 stocks)– Selectivity (3-ages and 4 fishery over 3 time periods for Selectivity (3-ages and 4 fishery over 3 time periods for
4 stocks =144)4 stocks =144)– Maturation (3 ages and 3 time periods=9*4=36)Maturation (3 ages and 3 time periods=9*4=36)– Initial Cohort abundance (3*4=12)Initial Cohort abundance (3*4=12)– Catchability by 3 time periods for 4 fisheries and 4 Catchability by 3 time periods for 4 fisheries and 4
stocks=48stocks=48
Total =350 parametersTotal =350 parameters
Tricks to Make Model ConvergeTricks to Make Model Converge
Maturation: Logistic by stock and time period Maturation: Logistic by stock and time period (Prior)(Prior)
Vulnerability: Logistic by stock, time period & Vulnerability: Logistic by stock, time period & fishery (Penalty).fishery (Penalty).
Recruitment: Stock recruit functions by Area Recruitment: Stock recruit functions by Area with time specific deviates (Prior).with time specific deviates (Prior).
Overall Model Fits by StockOverall Model Fits by StockSEAK (URB)
0
50,000
100,000
150,000
200,000
250,000
300,000
350,000
1979 1984 1989 1994 1999 2004Year
Cat
ch
WCVI (URB)
0
20000
40000
60000
80000
100000
120000
1979 1984 1989 1994 1999 2004Year
Cat
ch
TERMINAL CATCH (URB)
0
50,000
100,000
150,000
200,000
250,000
300,000
350,000
400,000
450,000
1979 1984 1989 1994 1999 2004
Year
Cat
ch
ESCAPEMENT (URB)
0
100,000
200,000
300,000
400,000
500,000
600,000
1979 1984 1989 1994 1999 2004
Year
ES
CA
PE
ME
NT
0
50000
100000
150000
200000
250000
300000
1979 1984 1989 1994 1999 2004
Year
Escapement (WCVI)
0
50,000
100,000
150,000
200,000
250,000
300,000
350,000
400,000
450,000
500,000
1979 1984 1989 1994 1999 2004
Year
Es
ca
pe
me
nt
TERMINAL CATCH (WCVI)
0
50,000
100,000
150,000
200,000
250,000
300,000
350,000
400,000
450,000
1979 1984 1989 1994 1999 2004
Year
Ca
tch
WCVI (WCVI STOCK)
0
50000
100000
150000
200000
250000
300000
350000
400000
1979 1984 1989 1994 1999 2004
Year
Ca
tch
SEAK (WCVI)
0
50,000
100,000
150,000
200,000
250,000
300,000
350,000
400,000
450,000
500,000
1979 1984 1989 1994 1999 2004
Year
Ca
tch
0
200
400
600
800
1,000
1,200
1,400
1984 1989 1994 1999 20040
20000
40000
1984 1989 1994 1999 2004
Year
SEAK (FRL)
0
200
400
600
800
1,000
1,200
1,400
1984 1989 1994 1999 2004
Year
Cat
ch
WCVI (FRL)
0
20000
40000
1984 1989 1994 1999 2004
Year
Cat
ch
Terminal
0
5,000
10,000
15,000
20,000
25,000
30,000
35,000
1984 1989 1994 1999 2004
Year
Cat
ch
Escapement
0
20,000
40,000
60,000
80,000
100,000
120,000
140,000
160,000
180,000
1984 1989 1994 1999 2004
Year
Esc
apem
ent
SEAK (QUEETS)
0
1,000
2,000
3,000
4,000
5,000
6,000
7,000
8,000
9,000
1979 1984 1989 1994 1999 2004Year
Cat
ch
WCVI (Queets)
0500
100015002000250030003500
1979 1984 1989 1994 1999 2004
Year
Cat
ch
Observed vs predicted Fit (TERM Catch)
0
2,000
4,000
6,000
8,000
10,000
12,000
14,000
16,000
1979 1984 1989 1994 1999 2004
Year
Cat
ch
Observed vs predicted Fit (ESC)
0
5,000
10,000
15,000
20,000
25,000
1979 1984 1989 1994 1999 2004
Year
Esc
apem
ent
RecruitmentRecruitmentURB & WCVI Recruitment
0
500,000
1,000,000
1,500,000
2,000,000
2,500,000
3,000,000
3,500,000
1975 1980 1985 1990 1995 2000 2005 2010
Age 2 Ocean Year
Nu
mb
ers
Queets & Fraser
0
50,000
100,000
150,000
200,000
250,000
300,000
350,000
400,000
1979 1984 1989 1994 1999 2004
Age 2 Ocean Year
Rec
ruit
men
t
SEAK vuln -URB
0.00
0.20
0.40
0.60
0.80
1.00
1.20
2 3 4 5age
1977-841985-951996-2002
SEAK (WCVI)
0.00
0.20
0.40
0.60
0.80
1.00
1.20
2 3 4 5age
1977-841985-951996-2002
SEAK (Queets)
0.00
0.20
0.40
0.60
0.80
1.00
2 3 4 5age
SEAK (FRL)
0.00
0.20
0.40
0.60
0.80
1.00
1.20
2 3 4 5age
Selectivity By Age in SEAKSelectivity By Age in SEAK
Exploitation in SEAK (1-exp(-F)) of the Vulnerable Population
0.00
0.10
0.20
0.30
0.40
0.50
0.60
0.70
0.80
1980 1985 1990 1995 2000 2005
Year
Rat
e
HR (URB)
HR(WCVI)
HR(QTS)
SEAK ExploitationSEAK Exploitation
WCVI SelectivityWCVI SelectivityWCVI (URB)
0
0.2
0.4
0.6
0.8
1
1.2
2 3 4 5Age
Vu
lner
abil
ity
1977-84
85-95
96-02
WCVI (FRL)
0
0.2
0.4
0.6
0.8
1
1.2
2 3 4 5Age
Vu
lner
abil
ity
1977-84
96-02
WCVI (WCVI)
0
0.2
0.4
0.6
0.8
1
1.2
2 3 4 5Age
Vu
lner
abil
ity
1977-84
85-95
96-02
WCVI (Queets)
0
0.2
0.4
0.6
0.8
1
1.2
2 3 4 5Age
Vu
lner
abil
ity
1977-84
85-95
96-02
WCVI ExploitationWCVI Exploitation
0.000
0.020
0.040
0.060
0.080
0.100
0.120
0.140
0.160
0.180
1980 1985 1990 1995 2000 2005
Year
Rat
e
HR (URB)
HR(QTS)
HR(FRL)
0.000
0.100
0.200
0.300
0.400
0.500
0.600
0.700
0.800
0.900
1980 1985 1990 1995 2000 2005
Year
Rat
e
HR (URB)
HR(WCVI)
HR(QTS)
HR(FRL)
Terminal SelectivityTerminal SelectivityTERMINAL (URB)
0
0.2
0.4
0.6
0.8
1
1.2
0 1 2 3 4 5Age
Vu
lner
abil
ity
1977-84
85-95
96-02
TERMINAL (FRL)
0
0.2
0.4
0.6
0.8
1
1.2
0 1 2 3 4 5Age
Vu
lner
abil
ity
1977-84
96-02
TERMINAL (WCVI)
0
0.2
0.4
0.6
0.8
1
1.2
0 1 2 3 4 5Age
Vu
lner
abil
ity
1977-84
85-95
96-02
TERMINAL (Queets)
0
0.2
0.4
0.6
0.8
1
1.2
0 1 2 3 4 5Age
Vu
lner
abil
ity
1977-84
85-95
96-02
Terminal ExploitationTerminal ExploitationTERMINAL EXPLOITATION
0.000
0.100
0.200
0.300
0.400
0.500
0.600
0.700
0.800
0.900
1.000
1980 1985 1990 1995 2000 2005
Year
Rat
e
HR (URB)
HR(WCVI)
TERMINAL EXPLOITATION
0.000
0.100
0.200
0.300
0.400
0.500
0.600
0.700
0.800
1980 1985 1990 1995 2000 2005
Year
Rat
e
HR(QTS)
HR(FRL)
Incorporating GeneticsIncorporating Genetics
Using catch composition estimates.Using catch composition estimates. Added to the Objective function using a Added to the Objective function using a
Multinomial Likelihood.Multinomial Likelihood. Explicitly taking the values from Genetic Explicitly taking the values from Genetic
Analysis.Analysis. Estimating proportions with assignment error Estimating proportions with assignment error
within the model structure.within the model structure.
4
1
4
1,,,, )ln(),|((
i fifififif pCpCLLn
SummarySummary
Spatially stocks and fisheries could be modeled in Spatially stocks and fisheries could be modeled in a single pool context using different selectivity a single pool context using different selectivity curves over stocks, fisheries and time.curves over stocks, fisheries and time.
Model complexity trade-off.Model complexity trade-off. Statistical catch at age models are more robust Statistical catch at age models are more robust
(empirical data and likelihood functions). (empirical data and likelihood functions). Can quantify the Uncertainty in our estimates, and Can quantify the Uncertainty in our estimates, and
use in predictive models.use in predictive models. Could add environmental forcing into the model.Could add environmental forcing into the model. Have the ability to incorporate genetic information.Have the ability to incorporate genetic information.
Next StepsNext Steps
Add genetics.Add genetics. Stratify by gear.Stratify by gear. Use age-length based estimates for selectivity by Use age-length based estimates for selectivity by
gear and area.gear and area. Add environmental covariates.Add environmental covariates. Quantify the scale at which fisheries and stocks Quantify the scale at which fisheries and stocks
could be aggregated for model.could be aggregated for model. Develop a migration module that connects Develop a migration module that connects
fisheries and stocks.fisheries and stocks.
AcknowledgementsAcknowledgements Mike Matylewich (CRITFC) for supporting Mike Matylewich (CRITFC) for supporting
this project.this project. Henry Yuen (USFWS) & Mark Maunder Henry Yuen (USFWS) & Mark Maunder
(IATTC) for help with the ADMB coding, (IATTC) for help with the ADMB coding, Robert Kope (NMFS) for initial review of Robert Kope (NMFS) for initial review of the approach.the approach.
John Carlile (ADFG), & members of the John Carlile (ADFG), & members of the Chinook Technical Committee (CTC-AWG).Chinook Technical Committee (CTC-AWG).
NOAA for funding this research.NOAA for funding this research.