Steelhead response to the removal of the Elwha River Dams

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Steelhead response to the removal of the Elwha River Dams Photo by John McMillan Pacific Coast Steelhead Management Conference March 22 2018 Walla Walla, WA

Acknowledgements Lower Elwha Klallam Tribe Mike McHenry, Ray Moses, Larry Ward, Mel Elofson, Sonny Sampson, Wilson Wells, John Mahan, Doug Morill, Robert Dohrn, Randall McCoy, Matt Beirne National Park Service Brian Winter, Anna Geffre, Josh Geffre, Heidi Hugunin, Phil Kennedy, Sam Brenkman, Pat Crain, Kathryn Sutton NOAA Fisheries George Pess, Martin Liermann, Todd Bennett, Steve Corbett, Oleksandr Stefankiv, Amilee Wilson, Zach Hughes, Tim Tynan, Eric Ward USGS Jeff Duda, Andy Ritchie, Chris Curran, Amy East, Jon Warrick WDFW Joe Anderson, Chris O Connell, Randy Cooper, Mike Gross, Andrew Claiborne & WDFW Fish Ageing Laboratory US Fish and Wildlife Service Roger Peters K Denton & Associates Keith Denton Trout Unlimited John McMillan US Bureau of Reclamation Jennifer Bountry, Tim Randle

Elwha River 833 km 2 watershed Elwha Dam built 1913 32 m tall River km 8 Glines Canyon Dam Built 1927 64 m tall River km 21 Pess et al. 2008 NW Science 115 km of habitat upstream of Elwha Dam site

Photo montage compiled by George Pess Photos from NPS time lapse camera

Photo montage compiled by George Pess Photos from NPS time lapse camera

Sediment release 21 million m 3 of sediment stored in former reservoirs 16 million m 3 in Lake Mills (upstream of Glines) 5 million m 3 in Lake Aldwell (upstream of Elwha) Approximately two-thirds evacuated from former reservoirs 90% delivered to coastal habitats Pools filled, 1.0 1.5 m increase in river channel height downstream of dams during peak of sediment wave At this point, erosion from reservoirs mostly complete Greatest remaining impact to salmon habitat in floodplain channels, not mainstem Lake Mills reservoir, Aug 28 2014 Andy Ritchie, NPS/USGS

Formazin Backscatter Units Formazin Nephelometric Units Turbidity Dam removal begins Glines rockfall blasting 2000 Elwha Dam removed Glines Canyon Dam removed FNU FBU 1500 1000 Approximate lethal threshold 500 0 6/2011 12/2011 6/2012 12/2012 6/2013 12/2013 6/2014 12/2014 6/2015 12/2015 6/2016 12/2016 6/2017 12/2017 Data from USGS

Elwha River mouth, estuary & nearshore Elwha River mouth 2006 Elwha River mouth 2015 0.5km 1km Slide courtesy of George Pess, NOAA

Monitoring and Adaptive Management 1. Preservation Prevent extinction when river conditions at times are lethal to fish 2. Recolonization Ensure continual access to habitat above former dam sites with some successful spawning 3. Local Adaptation Promote evolution of traits advantageous for natural river, increase life history diversity 4. Viable Natural Population Self-sustaining natural population productive enough to withstand harvest without hatchery supplementation

Triggers dictate movement between phases

Elwha hatchery steelhead program Goal: conservation of Elwha native steelhead population Current program is integrated broodstock management Eggs and fry collected 2005 2011, raised to reproductive maturity and spawned in captivity Currently switching from captive broodstock to adult returns to river Production goal = 175,000 age-2 smolts o Average release 2011 2016 = 141,935 smolts o Release site located at river km 3 Sources: Lower Elwha Klallam Tribe 2012 Steelhead Hatchery Genetic Management Plan (HGMP) Photo: John Mahan Lower Elwha Klallam Tribe HGMP Annual reports

Abundance Estimate abundance using SONAR

Adult steelhead abundance Steelhead SONAR abundance estimate 2500 Natural + hatchery origin Viable population goal 2000 Natural origin 1500 1000 Local adaptation goal 500 0 2012 2013 2014 2015 2016 2017 Recolonization goal Information for hatchery and natural origin steelhead was taken during species composition collections. The intent of species composition was not designed to estimate such proportions but is more of an indicator.

Strait of Juan De Fuca Productivity Elwha River screw trap locations Glines Canyon Dam Flow Little River 2012 Indian Creek 2013 Elwha Dam Mainstem Elwha 2005 = screw traps RKM 22 RKM 12 RKM 0

Estimated steelhead smolts outmigrants Smolt Productivity Elwha River, Indian Creek, & Little River Steelhead smolts 25,000 20,000 Elwha River Little River Indian Creek 15,000 10,000 5,000 0 2013 2014 2015 2016 2017 Year

Spatial distribution Elwha dam removed Glines Canyon dam removed Lower Elwha (below Elwha Dam site) Middle Elwha (between dams) Upper Elwha (above Glines Canyon)

Natural and Assisted Recolonization Year Indian Creek Fish relocated Redds Little River Fish relocated 2012 11 9 35 43 2013 0 24 88 47 2014 0 36 59 73 2015 0 6 0 36 2016 34 7 0 28 2017 0 16 0 37 Redds Data source: McMillan et al. 2018 Summary of 2017 winter steelhead surveys in the Elwha River Note 25% of Indian Creek and 98% of Little River are surveyed for spawners. Number of redds is not representative of the total number of spawners in each creek

Spatial distribution Steelhead spawning distribution 2016 Mouth to Elwha Dam Elwha Dam to Glines Canyon Upstream of Glines Canyon Source: McMillan et al 2017

Spatial distribution of hatchery mark rates Lower Elwha below hatchery 0-3 202 28 Lower Elwha above hatchery 3-8 33 14 Middle Elwha 8-21 6 11 Upper Elwha 21 + 0 3 Year River km Hatcheryorigin Naturalorigin Netting from SONAR and radio telemetry projects Data represent all encounters 2014 2017 Information for hatchery and natural origin steelhead was taken during species composition collections. The intent of species composition was not designed to estimate such proportions but is more of an indicator. Photo: Sam Brenkman

Former Glines Canyon Dam rockfall blast September/October 2015 Photos courtesy of Andy Ritchie, NPS Photos courtesy of Andy Ritchie, NPS

Diversity J. McMillan Summer run steelhead observations Summer steelhead first observed in newly accessible habitat Oct 2013 N = 72 counted during backcountry snorkel survey in September 2017 covering approximately 20 river km

Percent 90% Diversity Age structure determined from N = 207 adult steelhead 80% 70% 60% 50% 40% 30% 20% 10% 0% Saltwater age-1 Saltwater age-2 Saltwater age-3 1 2 3 Freshwater Age N = 9 distinct anadromous life history forms, accounting for repeat spawners

Diversity Winter-run entry timing Source: Denton et al. 2018 2017 SONAR Annual Report

Months/Years Hours/days Decades How long will recovery take? Turbidity Suspended sediment concentration Streambed particle size Juvenile fish density Invertebrate density & species composition Salmon populations Vegetation Wood recruitment Site (10 0 km) Reach (10 1 km) Watershed (10 2-10 3 km 2 )

Outlook for the future Encouraging signs: fish accessing areas upstream of dams, massive physical disturbance tapering off Steelhead populations far short of long term recovery goals First step is to ensure colonists reach newly accessible spawning and rearing habitats Interagency collaborative monitoring effort intended to adaptively manage Elwha fish populations Unique opportunity for salmon recovery

Thank you Photo by John McMillan