The Role of Large Woody Debris in Rocky Reach Reservoir

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The Role of Large Woody Debris in Rocky Reach Reservoir THE ROLE OF LARGE WOODY DEBRIS IN ROCKY REACH RESERVOIR First-Draft ROCKY REACH HYDROELECTRIC PROJECT FERC Project No. 2145 November 9, 2000 Prepared by: BioAnalysts, Inc. Boise, Idaho Prepared for: Public Utility District No. 1 of Chelan County Wenatchee, Washington Large Woody Debris TABLE OF CONTENTS SECTION 1: INTRODUCTION ................................................................................................. 1 SECTION 2: SOURCE OF LARGE WOODY DEBRIS............................................................ 3 SECTION 3: FUNCTION OF LARGE WOODY DEBRIS......................................................... 5 3.1 Submerged Large Woody Debris .................................................................................................................. 5 3.2 Floating Large Woody Debris ....................................................................................................................... 6 3.3 Large Woody Debris on the Floodplain ........................................................................................................ 7 SECTION 4: SUMMARY........................................................................................................... 9 SECTION 5: REFERENCES .................................................................................................. 11 Draft Study Report Rocky Reach Project No. 2145 November 9, 2000 Page i SS/2486 Large Woody Debris SECTION 1: INTRODUCTION Large woody debris (LWD) is an important component of aquatic ecosystems (Harmon et al. 1986; Maser and Sedell 1994; Gurnell et al. 1995). LWD provides physical structure that aquatic organisms use as habitat, and it alters water movements and hydrological processes (Triska and Cromack 1980; Franklin et al. 1981; Harmon et al. 1986; Maser and Sedell 1994). LWD affects the flow of organic matter from terrestrial ecosystems into surface waters (Franklin et al. 1981), and the transport of organic materials within aquatic ecosystems (Beschta 1979; Bilby and Ward 1991). The balance among inputs, decomposition rates, and removal processes determines the biomass of LWD inputs in freshwaters. Climate, soils, stream flow rates, stream gradient, topography (geomorphology), forest age, forest density, and community composition collectively determine the distribution and abundance of LWD in aquatic ecosystems (Harmon et al. 1986; Harmon and Chen 1991; Tyrrell and Crow 1994). Although LWD performs several essential functions in streams and rivers, the relative importance of each function varies with stream size. In small, steep headwater streams (first and second-order streams), LWD tends to dominate hydraulic processes by increasing the frequency and volume of pools, decreasing the effective streambed gradient, and increasing the retention of organic material and nutrients within the system (Bisson et al. 1987). In mid-order streams, LWD functions primarily to increase channel complexity and flow heterogeneity by anchoring the position of pools along the thalweg, creating backwater along the stream margin, causing lateral migration of the channel, and increasing depth variability (Maser et al. 1988). Another important function of LWD in mid-order streams includes the retention of carcasses and organic detritus, which provide nutrients to the biota within the stream and in the adjacent riparian area (Bilby et al. 1996; Cederholm et al. 1999). The function of LWD in high-order streams is less understood; however, historical records indicate that large debris jams once played a major role in floodplain and channel development on large rivers (Sedell and Luchessa 1981). In these high-order streams, LWD increased channel complexity by creating side channels, backwaters, and ponds, as well as refugia for aquatic organisms during winter storm events. LWD also trapped sediments on floodplains and in riparian zones during high flows. Schuett-Hames et al. (1994) describe three types of LWD: logs, rootwads, and large debris jams. To qualify as a log, a piece of wood must have a root system that is wholly or partially detached and is no longer capable of supporting the log’s weight. The wood must have a diameter of at least 10 cm for at least 2 m of its length. A root wad is defined as a piece of wood less than 2-m long (except for old-growth stumps), with a root system attached. It must be at least 20-cm diameter at the base of the stem where it meets the roots. The latter must be detached from their original position. A large debris jam is defined as an accumulation of 10 or more logs or rootwads in contact with one another. At Rocky Reach Dam, one could define LWD as any piece of wood that does not pass through the trash rack. Here, I follow the definition presented in Schuett-Hames et al. (1994). This paper investigates the source, function, and fate of LWD in the Rocky Reach Reservoir, emphasizing the function of LWD in the reservoir. Because there is virtually no information on LWD in Rocky Reach Reservoir, I draw on information from other systems, and rely mostly on Draft Study Report Rocky Reach Project No. 2145 November 9, 2000 Page 1 SS/2486 Large Woody Debris studies that examined the function of LWD in lakes. I found no studies that described the function of LWD in reservoirs of “run-of-the-river” hydroelectric projects. The Rocky Reach Natural Sciences Working Group will use this report to either formulate management decisions and plans or to recommend additional studies. Rocky Reach Project No. 2145 Draft Study Report SS/2486 Page 2 November 9, 2000 Large Woody Debris SECTION 2: SOURCE OF LARGE WOODY DEBRIS Large wood enters streams and rivers through two different pathways: (1) the steady toppling of trees as they die or are undercut by streamflow, and (2) catastrophic inputs associated with windstorms, mass failures, and debris torrents (Bisson et al. 1987; Cummins et al. 1994). Beavers (Castor canadensis) also contribute wood to streams (Maser and Sedell 1994). In addition, land management activities, such as logging and clearing, can influence the amount of wood entering streams. Once in the channel, LWD can either move downstream or stay in the channel or on the floodplain. Stream flows, size of the wood, and channel morphology determine whether the wood is transported or retained. In general, the larger the size of the wood, the greater its stability in the channel, since higher flows are needed to displace larger pieces (Bilby and Ward 1989). Wood enters the Rocky Reach project area from the riparian vegetation along the reservoir and from upstream locations. I found no estimates of the amount of LWD recruited annually to the project area. Whatever the total amount is, it would appear that riparian vegetation along the reservoir provides only a small fraction. Riparian vegetation occurs only intermittently along the margins of the reservoir and consists of grasses, forbs, shrubs, and deciduous trees (CPUD 1991). Generally, only trees provide a source of LWD. CPUD (1991) indicated that riparian vegetation types represent only about 40% of the shoreline. Presently, riparian vegetation types represent more than 40% of the shoreline, although the total amount is unknown (S. Hays, CPUD, personal communication). Therefore, the majority of the LWD recruited to the project area likely enters from upstream sources, such as the Entiat River and wood that passes Wells Dam. Until recently, large rafts of driftwood passed Wells Dam into Rocky Reach Reservoir. Currently, however, Douglas PUD mechanically removes a large fraction of the driftwood at their project (R. Klinge, DPUD, personal communication). Thus, the amount of LWD entering the project area from the Columbia River upstream from Wells Dam is relatively small. Once in the reservoir, LWD can become submerged in littoral1 areas or at the bottom of the reservoir, float at or near the water surface, strand on the floodplain, or pass through the dam. 1 The littoral zone extends from the shore just above the influence of waves and spray to a depth where light is insufficient for rooted aquatic vegetation (Goldman and Horne 1983). The pelagic zone is the deep-water area that extends beyond the littoral zone. Draft Study Report Rocky Reach Project No. 2145 November 9, 2000 Page 3 SS/2486 Large Woody Debris SECTION 3: FUNCTION OF LARGE WOODY DEBRIS LWD in aquatic systems can affect nutrient cycling and production, and provide refuges from predation (Wege and Anderson 1979; Lynch and Johnson 1989; Christensen et al. 1996). In lakes and reservoirs, it appears that both small- and large-scale processes affect the biological and physical functions of LWD (Maser and Sedell 1994). Small-scale processes control how LWD decomposes. In water, wood decomposes more slowly than on land because water-logging prevents oxygen from penetrating deeply into the wood (Harmon et al. 1986). Large-scale processes affect how LWD influence flows and channel structure (generally not important in reservoirs), and habitat for fish and invertebrates. Therefore, the function of LWD depends on its location within the reservoir. 3.1 Submerged Large Woody Debris Submerged LWD increases habitat structure, which provides cover and perhaps increases foraging opportunities for fish (Moring et al. 1989). Moring et al. (1986) studied the importance of submerged logs in a Maine reservoir and found that suckers (Catostomus spp.) and shiners (Notemigonus spp.) were attracted to LWD. Yellow perch (Perca flavescens), on the other hand, did not demonstrate a clear preference for LWD. In Rocky Reach
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