Spawning Distribution and Habitat Use of Adult Pacific and Western Brook Lampreys in Smith River, Oregon

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Spawning Distribution and Habitat Use of Adult Pacific and Western Brook Lampreys in Smith River, Oregon American Fisheries Society Symposium 72:173–189, 2009 © 2009 by the American Fisheries Society Spawning Distribution and Habitat Use of Adult Pacific and Western Brook Lampreys in Smith River, Oregon STEPHANIE L. GUNCKE L *, KIM K. JONE S , AND STEVEN E. JACOB S Oregon Department of Fish and Wildlife, 28655 Highway 34, Corvallis, Oregon 97333, USA Abstract.—Pacific lampreys Entosphenus tridentatus (formerly Lampetra triden- tata) and western brook lampreys L. richardsoni are observed in many coastal Oregon basins; however, few data are available to adequately describe their distribution and spawning habitat associations. To document landscape-scale distribution and habitat use of spawning adult lampreys, we conducted biweekly redd surveys at 62 random- ly selected sites in Smith River (Umpqua basin, Oregon). Characteristics of lamprey habitat were measured at the redd, habitat unit, and reach scales to quantify available and occupied habitat. Pacific lampreys were found primarily in wider, low-elevation streams, whereas western brook lampreys were more widespread but concentrated in headwater and low-order streams. At the unit scale, unit type and dominant substrate were weakly correlated to presence of spawning lampreys. Both species spawned in gravel rich habitats, predominantly pool tail-outs and low gradient riffles. This study infers habitat associations and broad-scale distribution within a coastal basin to assist in the design of monitoring strategies and population assessments at a regional scale. Introduction tioned the U.S. Fish and Wildlife Service to list Pacific, western brook, and two other lamprey Coastal Oregon populations of Pacific lamprey species as endangered in the Pacific Northwest Entosphenus tridentatus (formerly Lampetra and California (Nawa 2003). Even though the tridentata) and western brook lamprey L. rich- petition cited habitat losses due to reduced in- ardsoni are considered depressed due to habitat stream flows, water diversions, dredging, scour loss and passage problems (Close et al. 2002; and channnelization issues, pollution, and deg- Nawa 2003; ODFW 2006). The Pacific lamprey radation of riparian communities, the U.S. Fish was listed as an Oregon State sensitive species and Wildlife Service determined that the peti- in 1993 and in 1996 was protected through re- tion did not contain adequate information to striction of harvest (ODFW 2006). The western warrant a listing (USFWS 2004). The Oregon brook lamprey is not protected and has no spe- Department of Fish and Wildlife recently re- cial state status. Abundance of Pacific lampreys viewed the status of western brook and Pacific throughout the coast and Columbia River has lampreys and found populations to be “at risk” declined dramatically since the1960s. Dam of extinction (ODFW 2006) due to habitat loss, counts at Winchester (Umpqua River), Bonne- passage barriers and pollution. However, data ville (Columbia River), and Leaburg (McKenzie necessary to conduct a more thorough and de- River) dams show a dramatic decrease from his- tailed assessment are lacking. torical levels (Kostow 2002; Nawa 2003; ODFW Many of the lacking data are critical to the 2006). In 2003, 11 environmental groups peti- effective management and conservation of Or- * Corresponding author: stephanie.gunckel@oregonstate. egon’s coastal lamprey species. The Columbia edu River Basin Lamprey Technical Workgroup 173 174 gunckel et al. (CRBLTW 2005) and members of Columbia modified in order to determine an appropriate River Inter-Tribal Fish Commission (CRITFC sample frame and collect data in a quantitative 2004) have identified and prioritized critical data fashion. gaps for Pacific lamprey, many of which also ap- Our goal was to identify habitat variables ply to western brook lamprey. Among these are associated with spawning Pacific and western (1) methods to assess distribution and abun- brook lampreys in order to infer distribution dance of all life stages and appropriate techniques throughout coastal Oregon. The objectives of for monitoring population status; (2) population this study were to (1) determine distribution of structure and delineation; (3) population dy- spawning Pacific and western brook lampreys namics; (4) basic biology, including interspecific in the Smith River basin, (2) describe redds of and community level relationships; (5) limiting both species, and (3) describe associations of factors and threats, including passage issues, and spawning adults in relation to habitat unit- and (6) habitat needs and requirements. reach-scale habitat characteristics. In coastal basins, data describing distribu- tion and abundance of lampreys are rare despite Methods extensive and rigorous sampling since 1998 Study area under the Oregon Plan for Salmon and Water- sheds. Survey methods employed to determine This study was conducted in the Smith River, a status and trends in salmonid populations have tributary of the Umpqua River (Figure 1). The not proved applicable for lampreys. Surveyors study area consists of 463 km of main-stem collecting information on adult steelhead Onco- and tributary streams upstream of Smith River rhynchus mykiss during February through May Falls (river kilometer 48). The basin area above observe adult Pacific and western brook lam- Smith River Falls is approximately 525 km2. The prey individuals and redds, but the observations riparian community is dominated by red alder tend to be incidental rather than quantitative. Alnus rubra with an understory of sword fern Juvenile western brook and Pacific lampreys Polystichum munitum, salal Gaultheria shallon, are not observed by snorkelers or collected by and vine maple Acer circinatum. Smith River traditional electrofishing technology used for above the falls is inhabited by Pacific and west- salmonids. Although out-migrating juvenile ern brook lampreys, coho salmon O. kisutch, lampreys are collected in salmonid migrant Chinook salmon O. tshawytscha, steelhead, traps operated by the Oregon Department of coastal cutthroat trout O. clarkii, large-scale Fish and Wildlife, trap efficiency for lampreys sucker Catostomus macrocheilus, redside shiner is unknown (D. Jepsen, Oregon Department of Richardsonius balteatus, longnose dace Rhinich- Fish and Wildlife, personal communication). thys cataractae, and Umpqua pikeminnow Pty- Furthermore, these traps are not placed in ran- chocheilus umpquae. Land is owned predomi- domly selected watersheds such that findings nately by the U.S. Bureau of Land Management at trap sites cannot be extrapolated to other and private forest companies and managed for drainages. Habitat surveys conducted under timber harvest. the Oregon plan may be applicable, but habitat specific models are not available. Finally, with Sample site selection the exception of Winchester Dam on the North Umpqua River, counts of adult lampreys that In each of 2004 and 2005, 50 sample sites of pass dams are largely unavailable because dams 1,000 m were selected from a frame represent- in Oregon coastal basins are positioned in the ing the rearing distribution of coho salmon and upper portions of drainages. Existing sampling steelhead above Smith River Falls. Given the indicates that lampreys are present in coastal lack of available information regarding Pacific basins, but monitoring strategies need to be and western brook lamprey distributions, the spawning distribution and habitat use of lamprey 175 Figure 1. Smith River study area in Oregon and the Umpqua River basin. salmon and steelhead rearing sample frame surveyed by crews targeting steelhead trout offered the best starting point to describe po- where lamprey data were not consistently col- tential lamprey distribution in the basin. Sites lected; 1 site was not surveyable in 2005. Field were chosen in priority order using the variable crews were unable to incorporate the remain- probability. Stevens and Olsen (2004) general- ing sites (12 in 2004 and 18 in 2005) into the ized random tessellation stratified algorithm biweekly survey rotation. These sites were low and were randomly selected and spatially bal- priority and eliminating them did not disrupt anced ensuring an unbiased and representative the spatial balance of the remaining 31 sample sample. Site locations were unique each year. sites. Geographic coordinates of each site were plotted on U.S. Geological Survey 1:24K topo- Spawning surveys graphic maps and uploaded into a handheld Global Positioning System (GPS) unit. Field All sites were surveyed biweekly from between crews located the precise position of each site, March 29 and June 24, 2004, and March 28 and using a map, compass, and the GPS unit. The June 30, 2005. Newly observed lamprey redds coordinates represented the downstream end were measured, recorded, and flagged. For each of the sample site, which extended upstream a redd, crews noted species; measured length, channel distance of 1,000 m. width, depth of the redd, depth of the water, We surveyed 31 sites in 2004 and in 2005. water velocity, and distance to the nearest cov- Of the original sample draw of 50 sites in 2004, er; and conducted a pebble count. Cover was 2 were dry, 2 were not surveyable, and 3 were defined as any structure under which an adult 176 gunckel et al. lamprey could hide. Velocity was measured at Spawning survey analysis the midpoint of the lengthwise axis, on the thal- Basic descriptive statistics were used to describe weg side of the redd (Figure 2). Calipers were spawn timing, redd characteristics (median, used to measure the maximum diameter
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