Don Larsen, Abby Fuhrman, Deb Harstad, Dina Spangenberg, Brian Beckman NOAA Fisheries, Seattle Chris Kozfkay, Pete Hassemer IDFG
A “common garden” approach to understanding stock differences in Columbia basin hatchery minijack production
Outline • Introduction • Briefly review previous results from Harstad et al.
2014 as experimental lead in. • A “common garden” experiment to isolate
genetic vs. environmental effects on minijack rate • The effect of resource competition on minijack
rate in integrated and segregated stocks • Conclusions • A word about Red Fish Lake Sockeye
SUMMER CHINOOK LIFEHISTORY?
Hatchery spring/summer Chinook life history
Yearling Smolt 1+ yr (spring)
“Microjack”
Variation in Age of Male Maturity
Factors Affecting Age of Maturation
Mature male salmon
Genetics Environment
• temperature • food availability • food energy content
G x E interaction
Growth &
Body energy stores
The Hatchery environment can significantly influence age of maturation
“Sharpie”
Minijack
Jack
Age-4
Age-5
• 11-Ketotestosterone (11-KT) • Major androgen in teleost fish • Regulates spermatogenesis
11-KT
Onset of spermatogenesis
Early Spring (prior to Fall Spawn)
How to detect a minijack?
• Visual inspection of the testes
How to detect a minijack?
Summer (prior to Fall spawn)
Maturing Testes
Late Spring (prior to Fall Spawn)
Transactions of the American Fisheries Society 2014
9 Spring Chinook hatchery programs 5 Summer Chinook hatchery programs
• BYs: 1999-2010
• # of years sampled ranged from 1 to 12 years
Hatchery Facility
Acclimation Site
STOCK
Linear Regression: R2 = 0.63 p = 0.003
STOCK
Spring Chinook: Minijack rate is strongly correlated with size at release
% M
inija
cks
Size at Release (mm)
Spring Chinook: STOCK: LOCATION
Size at Release (mm)
% M
inija
cks
Integrated
Segregated
Integrated spring Chinook hatchery populations sampled had higher minijack
rates, even with smaller size at release
• These segregated programs have been in place for several decades
• An example of domestication selection?
Why do we care?
Ecological impacts Genetic impacts
Loss of adult production
Alter accuracy of Smolt-to-adult (SAR) return rates
Potential source of domestication
A common garden experimental approach
A valid question:
How do you know variation in minijack rate isn’t just due to rearing differences at the various hatcheries?
Winthrop
Imnaha Rapid R.
Carson
Sawtooth
Pahsimeroi McCall
Integrated Segregated Both
Common garden experiment
480 480 480 480 480 480 480
480 480 480 480 480 480 480
480
480
480
480
Snake R. Columbia R.
480
480
• Match growth rates • Compare minijack rates and
threshold size at age for maturation
Replicate tanks and different populations grew nearly identically
Date
15-18 fish per pound at release
Minijack rates varied by nearly 7-fold
Mean = 4.3%
4.6%
9.8%
7.7%
23.3%
19.0%
16.7%
28.4%
Life history
Size/Growth rate
Minijack
Smolt
Alternate life-history strategies have been modeled as threshold traits
Hazel et al. 1990
Hutchings and Myers 1994
Aubin-Horth and Dodson 2004
Piche’ et al. 2008
Logistic regression used to compare threshold growth rate for parr maturation
Thresholds vary among stocks
Common garden experiments with hybrid crosses create intermediate thresholds
Ilustrates the genetic component to the threshold
1 CAR 2 PAH-I 3 WIN 4 PAH-S 5 RAP 6 SAW-S 7 SAW-I 8 IMN
Pr (M
atur
atio
n)
Fork Length (mm)
Over a 20 mm difference in the size-at-age threshold (PMRN) among populations
20 mm
50%
What happened to the McCall fish in the Common Garden study?
McCall Competition Experiment • McCall INT and SEG stocks were
ponded in two separate 8 ft. diameter circulars in March
• PIT tagged 2400 fish on Aug. 26-28 (1200 per group)
• Combined Integrated and Segregated into 4 tanks: 2 Hi feed, 2 Lo Feed (600 per tank, 300 INT + 300 SEG) so they can complete.
INT/SEG
INT/SEG
Low Winter Feed (2X/wk)
INT/SEG
INT/SEG
High Winter Feed (3X/wk)
MAR APR MAY JUN JUL AUG SEP OCT NOV DEC JAN FEB MAR APR MAY Month
Common Garden and McCall combined analysis
McCall stocks (Hi feed) had the highest MJ rates
4.3% 4.6% 9.8%
7.7%
23.3%
19.0% 16.7%
28.4%
44.2%
42.5%
22.2%
13.2%
9% higher
What about sampling fish at the hatchery directly?
Sampling design
• BY 2013 Sawtooth and McCall (INT+SEG) • BY2014 Sawtooth, McCall, Pahsimeroi (INT+SEG)
and Rapid River (SEG) • 300 fish per population for length, weight, sex,
plasma for 11-KT just prior to release
Rapid R.
Sawtooth
Pahsimeroi McCall
Integrated Segregated Both
Seattle
35.1%
38.8% 38.7%
19.4%
4.1% 5.8% 4.7%
BY 2014 hatchery survey
We found variation in MJ rates among stocks and between brood years
BY 2013 hatchery survey
2.6%
35.7%
22.3%
15.4%
High BKD reported
How do rates at the hatcheries compare with rates in our laboratory scale studies?
Minijack rates in Hatchery surveys vs. Common Garden/McCall show some relationship, but not
significant
BY20
14 C
omm
on G
arde
n M
inija
ck R
ates
• Different hatchery stocks vary in their “sensitivity” to early male maturation
• Results suggest integrated stocks have a lower MJ/size threshold than segregated stocks
• McCall fish are very sensitive to early male maturation. Even modest Autumn-Winter rations resulted in high MJ rates
• Under lower ration conditions an integrated stock matured at a higher rate than a segregated stock
Conclusions
The Future • Further analyze current data • We took fin clips from all these fish for potential RAD
seq analysis for mapping genotype to phenotype in the future
• Hopefully sample hatchery stocks from BY 2015 to increase survey #’s especially in light of annual variation in some stocks
• Incorporate jack rates in to analysis • Explore early drivers of differences in threshold (i.e.
egg size, egg-fry metabolic rate, emergence time, others)
• Write peer review publications of results
• Monitor for early male maturation before release
• Growth profiles in the hatchery may need to be tailored to accommodate variation in sensitivity
Hatchery management implications
Frequent Question: If there are so many minijacks why aren’t adult sex rations more skewed towards females?
Wild Adult Escapement by Stock by Gender
Data provided by Carlos Camacho, IDFG
100 juveniles
50 females 50 males (40% minijacks)
50 female smolts 30 male smolts, 20 minijacks
Males return as jacks which have one less year in the ocean, thus higher survival Studies have shown that females experience higher exploitation rates in the ocean (Spidel et al. 1988; Holtby and Healy 1990)
Adult Gender Compensation
~60:40
Pretend No
smolt-to-adult mortality
50 female adults 30 male adults
80 adults
50/80 =62.5% Female, 30/80 =37.5% Male
A simplistic thought exercise for my simplistic brain?
Slide Number 1OutlineSlide Number 3Slide Number 4Slide Number 5How to detect a minijack?Slide Number 79 Spring Chinook hatchery programs �5 Summer Chinook hatchery programsSlide Number 9Spring Chinook: Minijack rate is strongly correlated with size at releaseSpring Chinook:Integrated spring Chinook hatchery populations sampled had higher minijack rates, even with smaller size at releaseSlide Number 13A common garden experimental approachSlide Number 15Slide Number 16Slide Number 17Slide Number 18Slide Number 19Slide Number 20Slide Number 21Slide Number 22Slide Number 23What happened to the McCall fish in the Common Garden study?McCall Competition ExperimentSlide Number 26McCall stocks (Hi feed) had the highest MJ rates What about sampling fish at the hatchery directly?Sampling designSlide Number 30We found variation in MJ rates among stocks and between brood yearsHow do rates at the hatcheries compare with rates in our laboratory scale studies?Minijack rates in Hatchery surveys vs. Common Garden/McCall show some relationship, but not significantConclusionsThe FutureHatchery management implicationsSlide Number 37Wild Adult Escapement by Stock by GenderSlide Number 39