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Size selection of adult Atlantic salmon at fish passage facilities on the Penobscot River, Maine. George Maynard 1 , Joseph Zydlewski 2,1 University of Maine, Dept. of Wildlife Ecology, Orono , ME 04469
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Size selection of adult Atlantic salmon at fish passage facilities on the Penobscot River, Maine George Maynard1, Joseph Zydlewski2,1 University of Maine, Dept. of Wildlife Ecology, Orono, ME 04469 U.S. Geological Survey, Maine Cooperative Fish and Wildlife Research Unit, Orono, ME 04469
Acknowledgements • Oliver Cox • Bill Halteman • Doug Sigourney • DimitryGorsky • Ed Hughes • Andrew O’Malley • Dan Stich • Ken Beland
Introduction • Fishways have existed on the Penobscot River since the mid 1800s • Not all fishways are created equal • Many factors influence how well salmon are able to pass through fishways
Introduction • Water temperature Maine DMR 2012 Adapted from Jonsson et al. 2007
Introduction • Water temperature • Water flow
Introduction • Water temperature • Water flow • Time of year
Introduction • Water temperature • River level • Time of year • Interannual variation
Introduction • Water temperature • River level • Time of year • Interannual variation • Salmon size
Salmon Size • Maximum swim speed is inversely related to size (Katopodis 1999) • Larger Atlantic salmon • require more attraction flow (Laine et al. 2002) • experience longer migratory delays (Jonsson et al. 2007)
Study Sites • Penobscot River system • Six hydropower dams • Monitored using PIT arrays • 2002-2004 • 2010-2012
Methods: Data Collection • Water temperatures from Maine DMR at the Veaziefishway • River height from USGS West Enfield gauge • Fork length measured during tagging at Veazie
Methods: PIT Arrays Downstream Upstream PIT Receiver Antenna 2 Antenna 1
Results: Overview Fish Length (cm) But is it significant? Relationships tested using Bayesian logistic regression.
Results • Four dams exhibited some size selection • Great Works • Milford • West Enfield • Mattaceunk (Weldon)
Results: Veazie • ΔDIC = 3 • n = 409 • Time of year and temperature
Results: Great Works • ΔDIC = 2 • n = 1471 • Fork length was the most important predictor of success
Results: Milford • ΔDIC = 5 • n = 1609 • Fork length was the most important predictor of success
Results: Howland • ΔDIC = 32 • n = 1241 • Annual Changes • Pike jump
Results: West Enfield • ΔDIC = 29 • n = 2444 • Annual impacts • Fork length still significant
Results: Mattaceunk (Weldon) • ΔDIC = 36 • n = 587 • Annual Changes • Fork length still significant
Discussion • Small dataset at VZ and HD • Influence of Year at WE and HD • Average fish size at HD • Upstream influence of delays • Strongest selection at lowermost dams
Why care? • Size may be indicative of a more successful individual • Feeding • Lifespan • Larger individuals can invest more energy into gamete production • Long term population impacts
Summary • Current changes in river management will benefit adult salmon • Construction of new Milford fishway • Removal of downstream dams and bypass at Howland • Further monitoring of fishways
Works Cited • Castro-Santos T. and B. Letcher. 2010. Modeling migratory energetics of Connecticut River American shad (Alosasapidissima): implications for the conservation of an iteroparous anadromous fish. Canadian Journal of Fisheries and Aquatic Science. 67:806-830. • Everhart H.W. and R.E. Cutting. 1968. The Penobscot River, Atlantic salmon restoration: key to a model river. Maine Atlantic Sea Run Salmon Commission. 8-14. • Fleming I.A. 1996. Reproductive strategies of Atlantic salmon: ecology and evolution. Reviews in Fish Biology and Fisheries. 6, 379-416. • Holbrook C.M., J. Zydlewski, D. Gorsky, S.L. Shepard, M.T. Kinnison. 2009. Movements of prespawn adult Atlantic salmon near hydroelectric dams in the lower Penobscot River, Maine. North American Journal of Fisheris Management. 29:495-505. • Jonsson, B., Jonsson, N. and Hansen, L. P. 2007. Factors affecting river entry of adult Atlantic salmon in a small river. Journal of Fish Biology 71, 943–956 • Kruschke J.K. 2011. Doing Bayesian data analysis: a tutorial with R and BUGS. Academic Press. • Laine, A., Jokivirta, T. and Katopodis, C. 2002. Atlantic salmon, Salmosalar L., and sea trout, Salmotrutta L., passage in a regulated northern river–fishway efficiency, fish entrance and environmental factors. Fisheries Management and Ecology 9, 65–77 • Lundqvist H., P. Rivinoja, K. Leonardsson, S. McKinnell. 2008. Upstream passage problems for wild Atlantic salmon (Salmosalar L.) in a regulated river and its effect on the population. Hydrobiologia. 602:111-127. • Noonan M.J., J.W.A. Grant, and C.D. Jackson. 2012. A quantitative assessment of fish passage efficiency. Fish and Fisheries. 13. 450-464. • Penobscot River Restoration Project (PRRP). 2013. Fact sheet. • Roscoe, D. W., Hinch, S. G., Cooke, S. J. and Patterson, D. A. 2011. Fishway passage and post-passage mortality of up-river migrating sockeye salmon in the Seton River, British Columbia. River Research and Applications 27, 693–705 • Sigourney D.B., J.D. Zydlewski, E. Hughes, and O. Cox. Transport, passage, and size selection of adult Atlantic salmon in the Penobscot River, Maine. In Review. • Werner R.G. Freshwater fishes of the northeastern United States. 2004. Syracuse University Press. 190-191. • Images from UMaine archive, Wikimedia Commons, and Bangor Daily News Archive