Columbia River Flows, Salmon, and Columbia River Flows, Salmon, and - - PowerPoint PPT Presentation
Columbia River Flows, Salmon, and Columbia River Flows, Salmon, and - - PowerPoint PPT Presentation
Columbia River Flows, Salmon, and Columbia River Flows, Salmon, and O Ocean Conditions Ocean Conditions O C C diti diti Kurt L. Fresh Kurt L. Fresh NOAA Fisheries, NWFSC NOAA Fisheries, NWFSC NOAA Fisheries, NWFSC NOAA Fisheries, NWFSC
Why Study Salmon in the Ocean? H i h R l d M i Ri ? How is that Related to Managing Rivers?
- Understand the role of ocean conditions on
U de sta d t e o e o ocea co d t o s o growth and survival of Columbia River salmon.
– Provide the context for recovery actions in the Basin. – Determine the relative roles of hydrosystem, freshwater and marine factors on salmon survival in the Columbia River Basin the Columbia River Basin.
- Support the FCRPS, BIOP.
- Provide information that can be used in adaptive
Provide information that can be used in adaptive management of fish and the hydrosystem in the Columbia River Basin.
Ocean survival vs a s mmar metri
Snake River Salmon
SAR (Smolt to Adult) (survival from LGR to LGR) versus: In‐river survival
(LGR to BON)
Ocean survival
(BON to BON)
a summary metric
- f ocean conditions
Hatchery Spring Chinook
R)
- BON)
Wild Steelhead
Survival (SAR vival (BON to Total S Ocean Surv
Hatchery Steelhead
Survival data include 2000‐2009 and come from: http://www.cbr.washington.edu/trends/index.php
In‐river Survival Ocean Survival Ocean Indicator *
* This metric is a combination of food resources and other physical and biological conditions in the ocean
Why Study Salmon in the Ocean?
1. Absolute survival in all life stages is important for conservation and recovery
- In‐river survival may not contribute much to forecasts,
but 50% in‐river survival still reduces returns by 50%
- Upstream of Lower Granite Dam (LGR): adult survival and
f l l h hl bl d h egg‐fry‐smolt survival are highly variable and have a strong influence on population dynamics 2. Variability in survival is important for forecasting
- Most of the variability in SAR (survival from LGR to LGR)
- Most of the variability in SAR (survival from LGR to LGR)
comes from variability in the ocean
- In‐river variability is more important for steelhead than
for Chinook salmon for Chinook salmon
HOW TO BE A SALMON HOW TO BE A SALMON Variations on a Theme
- Differences between species (7).
- Differences within species between groups of
Differences within species between groups of individuals‐ populations (dozens)
– A more or less discrete breeding group of salmon.
- Spawning location
Spawning location
- Body size and age at maturity.
- Timing of life history events
- Differences between individuals within a
population
– Life history type.
The Ocean Program The Ocean Program
- BPA Funding
BPA Funding
– NOAA + OSU, OHSU, UW: 1998 to present Canada DFO 1999 to 2012 (phasing out) – Canada DFO, 1999 to 2012 (phasing out) – Kintama, 2005‐2011
Oth F di
- Other Funding
– NOAA
- In kind (salary, equipment)
- Other sampling platforms.
Sampling methods
- Juvenile salmon with
surface trawl: sometimes with a small mesh liner
- Plankton nets
- Other: buckets, CTDs
- Acoustics
- Bird and marine mammal
- bservations
48° N
Sampling Design
48 N
La Push Queets River
Washington
- Newport Line biweekly
- ceanographic and
47° N
Grays Harbor Will B
g p plankton sampling since 1996 (17th year)
46° N
Willapa Bay Columbia River
- Juvenile salmon sampling
in May June and
Cape Meares Cape Falcon
Oregon
in May, June and September since 1998 (15th year)
45° N
Cascade Head
Newport
(15th year)
126° W 125° W 124° W 123° W
^ _
Cape Perpetua
Newport
What We Have Learned What We Have Learned
- Learned a lot about salmon in the ocean
Learned a lot about salmon in the ocean. Some highlights.
- We can use our science to help identify ways
- We can use our science to help identify ways
that we can affect salmon performance (growth/survival) during early ocean life (growth/survival) during early ocean life (adaptive management) I j l h f h
- Its not just salmon; there are uses of other
data from the ocean project.
Conceptual Model
H2
Salmon
H1 H3: Plume Structure H3: Plume Structure H4: Hydropower System H5: Freshwater vs. Ocean Survival H5: Freshwater vs. Ocean Survival
What Have We Learned: Some Highlights
The First Several Months at Sea Are Critical to Many Columbia y River Salmon Stocks An Example: Early Ocean Growth is Early Ocean Growth is Critical to Survival of Yearling Stocks
- f Chinook Salmon
Variability Between and Within Stocks i H h R d O in How they Respond to Ocean Conditions
Spatial distribution is stock‐specific stock specific
Snake River Sub‐yearling Fall Chinook Snake River Yearling Spring Chinook
We Can Use Our Science We Can Use Our Science
- We can use our understanding of how the
We can use our understanding of how the
- cean influences juvenile salmon to:
– Affect the environment or habitats the fish – Affect the environment or habitats the fish
- ccupy.
– Affect the fish Affect the fish – Predict or forecast how fish will respond to ocean conditions. conditions.
Fl E di O Vi Flow‐ Expanding Our View
Flow ‐ The Plume
F h t f th C l bi Ri i i ith th Freshwater from the Columbia River mixing with the ocean
- River water
di h d discharged into coastal
- cean every
WA
- utgoing tide
- Freshwater
pool pool propagates
- ffshore
OR Synthetic aperture radar image, July 2003
Courtesy D. Jay, Portland State University
Three marine regions of the plume
Far field plume days Near field plume‐ hours y Recirculating plume Hours to days
Photo off North Head Lighthouse, looking west
Plume is not Simply Local and Focused Near the Mouth of the River Near the Mouth of the River
Columbia River Plume
8‐day Composites : May 1999 day Composites : May 1999
The Plume is Dynamic in Space and Time The Plume is Dynamic in Space and Time
y p y y p y
Plume Affects Growth and Adult Returns
Snake River spring Chinook
‐2 yr) eturns (‐
Mid‐upper Columbia River spring Chinook
Adult re
pp p g from Tomaro et al. 2012 and
- J. Miller et al. (In prep.)
Predators
ALTERNATIVE PREY ABUNDANT NOT
Plume can Affect
Forage Fish Abundant NOT Juvenile Salmon
Avian Predation
Percent Eaten by Predators Percent Eaten by Predators
Low Salinity Large Plume
ALTERNATIVE PREY ABUNDANT IS
Predators
Forage Fish Abundant ARE Juvenile Salmon
Percent Eaten by Predators
High Salinity S ll Pl
Predators
Percent Eaten
Small Plume
We Affect Attributes of the Plume We Affect Attributes of the Plume
- About 44% of variability in plume
volume is explained by Bonneville river discharge. Coastal winds explains ~30% of the plume b l variability
- We can predict features of the
plume in advance. – Weeks to years. – Due to climate change, restoration.
From Antonio Baptitsta, OHSU
River flow Total fish abundance Caspian tern predation
l i i
p p
- n salmon
Flow is Important in The Estuary
www.birdresearchnw.org
We Can Affect the Fish
- We can manipulate
We can manipulate
– Time, size, abundance of hatchery fish being released released. – How hatchery and wild fish move downstream and how fast they get to the ocean: flow/spill, and how fast they get to the ocean: flow/spill, barging
Interannual variation in timing of marine entry Snake River Mid‐upper Columbia River
Forecasting Forecasting
- Adaptive management When should we be
Adaptive management. When should we be concerned about low returns and what can we do about it do about it.
- Harvest.
H h
- Hatchery management.
- Life cycle modeling and early warning
indicators.
- Understanding ocean ecology of salmon.
g gy
Develop Forecasting Models‐ First Generation
Ecosystem Indicators 1998 1999 2000 2001 2002 2003 2004 2005 2006 2007 2008 2009 2010 2011 2012
PDO (December-March)
14 6 3 10 7 15 9 13 11 8 5 1 12 4 2
PDO (May-September)
9 4 6 5 10 14 13 15 11 12 2 8 7 3 1
ONI Jan-June
15 1 1 6 11 12 10 13 7 9 3 8 14 4 5
46050 SST (May-Sept)
13 8 3 4 1 7 15 12 5 14 2 9 6 10 11
NH 05 Upper 20 m T winter prior (Nov-Mar)
15 9 6 8 5 12 13 10 11 4 1 7 14 3 2
NH 05 Upper 20 m T (May-Sept)
13 10 12 4 1 3 15 14 7 8 2 5 11 9 6
NH 05 Deep Temperature
15 4 8 3 1 11 12 13 14 5 2 10 9 6 7
NH 05 Deep Salinity
15 3 6 2 5 13 14 9 7 1 4 11 12 8 10
Copepod Richness Anomaly
15 2 1 6 5 11 10 14 12 9 7 8 13 3 4
- N. Copepod Biomass Anomaly
14 10 6 7 4 13 12 15 11 9 3 8 5 1 2
- S. Copepod Biomass Anomaly
15 3 5 4 2 10 12 14 11 9 1 7 13 8 6
Biological Transition
14 10 6 5 7 13 9 15 12 2 1 4 11 3 8
Winter Ichthyoplankton
15 7 2 4 5 14 13 9 12 11 1 8 3 10 6
Chinook Juv Catches (June)
14 3 4 12 8 10 13 15 9 7 1 5 6 11 2
Coho Juv Catches (Sept)
11 2 1 4 3 6 12 14 8 9 7 15 13 5 10
Mean of Ranks
13.8 5.5 4.7 5.6 5.0 10.9 12.1 13.0 9.9 7.8 2.8 7.6 9.9 5.9 5.5
RANK of the Mean Rank
15 4 2 6 3 12 13 14 10 9 1 8 11 7 4
Principle Component Scores (PC1)
6.56
- 2.22
- 2.95
- 1.60
- 2.12 2.08 3.12
4.21 1.10 -0.30 -4.39 -0.91 1.13 -1.76 -1.96
Principle Component Scores (PC2)
- 0.51
0.04
- 0.24
- 0.76
- 1.96 -1.53 2.55 -0.43 -0.66
1.07 -0.50 0.96 -0.74 1.36 1.35
Ecosystem Indicators not included in the mean of ranks or statistical analyses Physical Spring Trans (UI Based)
3 6 14 12 4 9 11 15 9 1 5 2 7 8 13
Upwelling Anomaly (Apr-May)
7 1 13 3 6 10 9 15 7 2 4 5 11 13 11
Length of Upwelling Season (UI Based)
6 2 14 9 1 10 8 15 5 3 7 3 11 13 11
g p g ( )
6 9 8 5 5 3 3 3
NH 05 SST (May-Sept)
10 6 5 4 1 3 15 13 8 12 2 14 9 7 11
Copepod Community Structure
15 3 5 7 2 12 11 14 13 8 1 6 10 9 4
C t t B ill
( l h )
2
Spring Chinook Salmon Adult Returns
Counts at Bonneville (plus harvest)
R2 = 0.81
- Oceanic Nĩno Index
- Pacific Decadal Oscillation
L l fi h i iti 2013= 221,000
- Larval fish species composition
Actual= 113,000 Actual= 113,000
Counts at Ice Harbor
R2 = 0.82
- Copepod species richness
- Copepod species composition
2013= 97 000
- Timing of biological transition
97,000
Spring Chinook Salmon Adult Returns Spring Chinook Salmon Adult Returns
Counts at Priest Rapids Dam
R2 = 0.69
- Pacific Decadal Oscillation
- Larval fish biomass
- Larval fish species composition
2013= 20,000
Adaptive Management: In Season Forecasting
Early Warning System
More salmon survive when there are more winter fish larvae (for example: sand lance, smelts, rockfish, anchovies)
- Estimates of winter fish larvae biomass can be made as early as April
350000
- Estimates of winter fish larvae biomass can be made as early as April
Bonnevile Dam rs
250000 300000 350000 2000 2001 2002
R2 =70.7%; p = 0.0007
dult returns to B 5/31 lag 2 year
150000 200000 2003 2004 2005 2006 2007 2008
ing Chinook ad 3/15-
50000 100000 2009 2010
Winter ichthyoplankton biomass of salmon prey (log C mg/m3)
- 2.6
- 2.4
- 2.2
- 2.0
- 1.8
- 1.6
- 1.4
- 1.2
- 1.0
Spr
Climate Change and The Ocean Program Climate Change and The Ocean Program
Evidence of climate change that we are already Evidence of climate change that we are already seeing:
- Increased variability of the PDO (since 1998, changes in sign
y ( , g g every 5 years rather than every 20‐30 years as seen in the past). U lli i th th C lif i C t i t ti l t
- Upwelling in the northern California Current is starting later
and the length of the upwelling season is shorter.
10 15 20
Pacific Decadal Oscillation
s PDO
10
- 5
5 10
Spring Chinook Salmon 123,131 average count
r of adults pawn
300000 400000 1970 1980 1990 2000 2010
- 15
- 10
- f numbe
rning to s
- 100000
100000 200000
Ad l S i Chi k B ill i
1970 1980 1990 2000 2010
Anomaly retu
- 200000
100000
Adult Spring Chinook at Bonneville continue to track the PDO although the recent highly negative (and near record values) of the PDO have not resulted in record returns of Chinook -- recall that d i 2001 d 2002 record returns were seen in 2001 and 2002.