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Photo: Carey Smith, Pacific Coast Joint Venture, Vancouver, WA
Wetland Recovery and Salmon Population Resilience:
A Case Study in Estuary Ecosystem Restoration
Daniel L. Bottom NOAA NW Fisheries Science Center, Newport, OR
Kim K. Jones, Trevan J. Cornwell, Staci Stein Oregon Department of Fish and Wildlife, Corvallis, OR
Lance A. Campbell
Washington Department of Fish and Wildlife, Olympia, WA
From Reimers 1973
• Fry migrants
• Yearling migrants
• Subyearling migrants
• Subyearling migrants (mid summer)
• Subyearling migrants (late summer/fall)
Life history diversity in Chinook salmon
• Stream rearing (~1 ½ years) • Ocean rearing (~1 ½ years)
Conventional life history of Coho salmon
High Diversity
Reduced Diversity
Resilience of Salmon with Diverse Life Histories
Salmonid Response
Environmental variability
Photo: Carey Smith, Pacific Coast Joint Venture, Vancouver, WA
Objective
• Juvenile habitat use and performance within the estuary (residency, foraging success, growth)
• Population response within the basin (life history diversity, production, resilience)
Determine whether recovery of tidal wetlands in Salmon River estuary has benefited Chinook and coho salmon, as indicated by:
• Chinook salmon study (1998 – 2005) • Coho salmon study (2008 – 2011) • Pre-hatchery survey (1975-77)
Salmon River Research
Salmon River Basin
• 195 km2 watershed
• Estuary area 800 ha
• Head of tide ~ Rkm 6.5
• Fish hatchery at Rkm 8
• Estuary protection: Cascade Head Scenic Research Area (1974)
Reference
1987 1996
1978
Salmon River Estuary Marsh Restoration
>175 ha restored
2011
Life-cycle perspective:
• Juvenile abundance in streams (coho)
• Migration from watershed
• Estuary habitat use, movement, timing and CPUE, growth
• Adult returns (spawner surveys)
• Life history reconstruction: − juv, adult otoliths − PIT tags (coho) − Survival (coho)
Sampling at estuary mouth to collect ocean-bound juveniles
Reconstruct life histories of juveniles and adults from otolith chemistry
Life History Variation in Juvenile Salmon
• Strontium indicator of salt-water entry
• Back-calculated size at estuary entry based on otolith:fish size relationship
• Growth rates from daily increments
1975
0
20
40
60
80
100
1976
CPU
E (n
umbe
r/sei
ne h
aul)
0
20
40
60
80
100
1977
Mar May Jul Sep Nov
0
20
40
60
80
100
Lower estuary Mid estuary Upper estuary 75' seine (1977) Upper estuary 125' seine (1977)
2000
0
20
40
60
80
100
2002
Mar May Jul Sep Nov
0
20
40
60
80
100
2001
CPU
E (n
umbe
r/sei
ne h
aul)
0
20
40
60
80
100
Lower estuary Mid estuary Upper estuary
Chinook life history diversity has expanded with increased estuary rearing opportunity
E Fry ER<30d
E Fry ER>30d
Spring Migrant ER<30d
Spring Migrant ER> 30d
Summer Migrant ER<30d
Summer Migrant ER>30d
Fall Migrant ER< 30d
Fall Migrant ER> 30d
Early Fry
Spring
Summer Summer
Fall
Size at Estuary Entry (mm) Emergent Fry < 45 Spring (MAM) 47 – 64 Summer (JJA) 55 – 96 Fall (SON) 97 – 109
Life histories of outmigrating juvenile Chinook
(adapted from Volk et al. 2010)
Juvenile Life Histories of Returning Adult Chinook
Run Year 2004 (n=145)
Run Year 2005 (n=85)
Size at Estuary Entry (mm FL)
• All 4 migrant types contributed to surviving adults
• 25 – 40% of spawners were spring fry migrants that were rare or absent when the marshes were diked
(L. Campbell unpubl. data)
PIT Array, Smolt Trap
Coho Population Studies Salmon River 2008-2011
Jones et al. 2014
CPUE upper Salmon R. estuary
yearling
subyearling
• Yearlings in upper estuary in the spring
• 27% of tagged yearlings used 96 Marsh (2010)
• Contrary to the conventional coho life history, subyearlings reared in estuary wetlands
• Fry entered in spring; parr were present late fall and winter
Juvenile coho use of upper estuary and wetlands
Diverse juvenile coho life histories in Salmon River
Yearling Fry Nomad Parr
Juvenile Migrant Type
Rearing Environment
Stream and Tidal Fresh
Estuary
Ocean
(Jones et al. 2014)
Juvenile Life Histories of Returning Adult Coho
• 20-35% of returning adults had reared in the estuary • Estuary life histories were absent when marshes were diked • Estuary restoration has increased coho life history diversity as
well as production
Yearling Nomad Fry Parr
Estuary rearing types
(Jones et al. 2014)
Coho life history diversity has expanded with increased estuary rearing opportunity
(Jones et al. 2014)
Lessons from Salmon River
• Restoring estuary habitat has enhanced life history expression in both Chinook and coho salmon
• Coho that leave natal streams as subyearlings are not lost to the population but use the estuary
• Estuary life histories linked to restored wetlands contributed 25-40% of adult Chinook and 20-35% of adult Coho produced in Salmon River
• Life history diversity (and the habitat opportunities that support it) is fundamental to the productivity as well as the resilience of salmon populations
Case Studies in Salmon Resilience