Salmonid early response to restored freshwater floodplain

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Western Washington University Western CEDAR Salish Sea Ecosystem Conference 2014 Salish Sea Ecosystem Conference (Seattle, Wash.) May 1st, 10:30 AM - 12:00 PM Salmonid early response to restored freshwater floodplain Erin Morgan Wetland Ecosystem Team, emorgan2@uw.edu Jeff Cordell University of Washington Lauren Rich Upper Skagit Indian Tribe of Washington Follow this and additional works at: https://cedar.wwu.edu/ssec Part of the Terrestrial and Aquatic Ecology Commons Morgan, Erin; Cordell, Jeff; and Rich, Lauren, "Salmonid early response to restored freshwater floodplain" (2014). Salish Sea Ecosystem Conference. 141. https://cedar.wwu.edu/ssec/2014ssec/day2/141 This Event is brought to you for free and open access by the Conferences and Events at Western CEDAR. It has been accepted for inclusion in Salish Sea Ecosystem Conference by an authorized administrator of Western CEDAR. For more information, please contact westerncedar@wwu.edu.

Salmonid Early Response to a Restored Freshwater Floodplain Erin Morgan Wetland Ecosystem Team UW School of Aquatic & Fishery Sciences Salish Sea Ecosystem Conference Seattle, WA May 1, 2014

Introduction GOAL: Reconnect wetland & floodplain to enhance salmonid spawning/rearing & increase production How do off-channel habitats benefit salmon? Sommer et al. 2001, p. 330 Jeffres et al. 2008, p. 455 http://californiawaterblog.com/2011/06/02/frolicking-fat-floodplain-fish-feeding-furiously/ Denser prey resources = enhanced growth Sommer et al. 2001, Jeffres et al. 2008, Limm & Marchetti 2009, Bellmore et al. 2012

Questions & Criteria FOCUS: Evaluate function of main channel, wetland, and floodplain habitats w.r.t. rearing & foraging 1.) Evaluate prey resources (capacity to support production) What is the quantity/composition across habitats? 2.) Evaluate fish density (opportunity to access capacity) 3.) Evaluate diet composition & fish condition (realized function) Can fish access restored capacity? Is fish density related to prey resource availability? Is there a measureable physiological benefit (increased fitness) in any habitat?

http://lewseportfolio.wordpress.com/fry-parr-the-elective-courses/

Criteria 1: Prey resources Average Density (#/m 3 ) 120 100 80 60 40 20 0 2R 3H 3N 4C 4H 4S Site All reaches are similar in prey density and composition.

Criteria 2: Coho Density/ Abundance Average estimated density (fish/m 2 ) 8 6 4 2 0 Glide Pool Riffle 2R 3H 3N 4C 4H Site Coho densities follow expected patterns across the project. CPUE (fish/s) 1.8 1.5 1.2 0.9 0.6 0.3 0 Floodplain Mud Sand January February March April May June July August Month Coho can access floodplain & wetland capacity.

Criteria 3: Diet Composition/Fitness Average % IRI 100% 80% 60% 40% 20% 0% Habitat Site 49 Pool 49 31 37 44 45 39 42 47 35 18 19 40 37 40 Riffle Pool Riffle Pool Riffle Glide 2 Reference 3 Historic 3 New 4 Channel 4 Historic 4 Sheetflow Pool Riffle Pool Riffle Floodplain Mud Sand Other Trichoptera immature Plecoptera nymph Hemiptera Ephemeroptera nymph Chironomidae adult Chironomidae pupa Chironomidae larva Diptera Collembola Coleoptera Annelida Flies (Diptera), especially midge larvae, are dominant diet item Diet assemblage generally matches drift IR similar across sites/habitats No evidence of prey subsidy in off-channel habitats.

Discussion How is the restoration doing? Hansen Creek vs. Other Studies Capacity: Prey resources are similar across all sites Channel drift: avg.~ 6x denser (Wipfli and Gregovich 2002) Floodplain abundance: ~30x higher (pilot) Opportunity: Coho are using habitats as expected across the site Coho density: avg. ~ 6-10x denser (pools, summer) (Nielsen 1992) Realized Function: Diet composition as expected, no IR differences. Diet composition: dominated by midges, which other studies agree is most important diet item for coho fry (Higgs et al. 1995) IR: No difference between sites vs. significantly higher IR in FP

Conclusions & Recommendations Reference and restored sites are biologically similar after only 3 years. Prey resources may not be limiting coho salmon production. Floodplain habitat may still serve other important functions for salmon. Where do we go from here? Changes in vegetation & hydrology will be ongoing Monitor again in 5-10 years

Acknowledgments Wetland Ecosystem Team Jeff Cordell Jason Toft Elizabeth Armbrust Michael Caputo Aaron David Emily Howe Brittany Jones Maria Karm Claire Levy Stuart Munsch Bob Oxborrow Alyssa Suzumura USIT Lauren Rich Lisa Hainey Josh Adams Mike Bartlett Danielle Raposa Skagit Co. Public Works Dept Emily Derenne Jeff McGowan Volunteers Katie Dowell Andrew Annanie UW School of Aquatic & Fishery Sciences Katherine Armintrout Kristin Connelly Funding Ava Fuller Provided by the Upper Skagit Indian Tribe, through EPA s Puget Sound Tribal Capacity Program grant

References Baxter, CV, KD Fausch, and WC Saunders. 2005. Tangled webs: reciprocal flows of invertebrate prey link streams and riparian zones. Freshwater Biology 50: 201-220. Beechie, T, E Beamer, and L Wasserman. 1994. Estimating coho salmon rearing habitat and smolt production losses in a large river basin, and implications for habitat restoration. North American Journal of Fisheries Management 14(4): 797-811. Bellmore, RJ, CV Baxter, AM Ray, L Denny, K Tardy, and E Galloway. 2012. Assessing the potential for salmon recovery via floodplain restoration: a multitrophic level comparison of dredge-mined to reference segments. Environmental Management 49: 734-750. Cloe, WW and GC Garman. 1996. The energetic importance of terrestrial arthropod inputs to three warm-water streams. Freshwater Biology 36: 105-114. Crouse, MR, CA Callahan, KW Malueg, and SE Dominguez. 1981. Effects of fine sediments on growth of juvenile coho salmon in laboratory streams. Transactions of the American Fisheries Society 110(2): 281-286. Higgs, DA, JS Macdonald, CD Levings, and BS Dosanjh. 1995. Nutrition and feeding habits in relation to life history stage. In: C Groot, L Margolis, and WC Clarke, eds. Physiological ecology of Pacific salmon. Vancouver (BC): UBC Press. 510 pp. Jeffres, CA, JJ Opperman, and PB Moyle. 2008. Ephemeral floodplain habitats provide best growth conditions for juvenile Chinook salmon in a California river. Environmental Biology of Fishes 83: 449-458. Limm, MP and MP Marchetti. 2009. Juvenile Chinook salmon (Oncorhynchus tshawytscha) growth in off- channel and main-channel habitats on the Sacramento River, CA using otolith increment widths. Environmental Biology of Fishes 85: 141-151. Mason, JC. 1976. Response of underyearling coho salmon to supplemental feeding in a natural stream. The Journal of Wildlife Management 40(4): 775-788. Nielsen, JL. 1992. Microhabitat-specific foraging behavior, diet, and growth of juvenile coho salmon. Transactions of the American Fisheries Society 121(5): 617-634. Quinn, TP. 2005. The behavior and ecology of Pacific salmon and trout. Seattle (WA): University of Washington Press. 378 pp. Simenstad, CA and JR Cordell. 2000. Ecological assessment criteria for restoring anadromous salmonid habitat in Pacific Northwest estuaries. Ecological Engineering 15: 283-302. Sommer, TR, ML Nobriga, WC Harrell, W Batham, and WJ Kimmerer. 2001. Floodplain rearing of juvenile Chinook salmon: evidence of enhanced growth and survival. Canadian Journal of Fisheries and Aquatic Sciences 58: 325-333. Waters, TF. 1972. The drift of stream insects. Annual Review of Entomology 17: 253-272.