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Biological Opinions - Bureau of Reclamation

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CDFW’s Restoration Manual (Flosi et al. 2010) to maximize the benefits <strong>of</strong> each project while<br />

minimizing effects to salmonids. Most restoration projects are for the purpose <strong>of</strong> restoring<br />

degraded salmonid habitat and are intended to improve instream cover, pool habitat, spawning<br />

gravels, and flow levels; remove barriers to fish passage; and reduce or eliminate erosion and<br />

sedimentation impacts. Others prevent fish injury or death, such as diversion screening projects.<br />

Although some habitat restoration projects may fail or cause small losses to the juvenile life<br />

history stage <strong>of</strong> listed salmonids in the project areas during construction, most <strong>of</strong> these projects<br />

are anticipated to restore coho salmon habitat over the long-term.<br />

The Restoration Manual (Flosi et al. 2010) provides design guidance and construction techniques<br />

that facilitate proper design and construction <strong>of</strong> restoration projects. As discussed earlier in the<br />

Effects to SONCC Coho Salmon ESU Critical Habitat section (i.e., section 11.4.2.3), NMFS<br />

expects the habitat restoration activities will amount to an annual average <strong>of</strong> about 71 percent<br />

effectiveness.<br />

a. Instream Habitat Improvements<br />

In addition to the habitat benefits discussed earlier in the Effects to SONCC Coho Salmon ESU<br />

Critical Habitat section (i.e., section 11.4.2.3), stream enhancement techniques aimed at<br />

reducing juvenile displacement downstream during winter floods and at providing deep pools<br />

during summer low flows could substantially increase stream rearing capacity for coho salmon<br />

(Narver 1978). Presence and abundance <strong>of</strong> LWD is correlated with growth, abundance and<br />

survival <strong>of</strong> juvenile salmonids (Fausch and Northcote 1992, Spalding et al. 1995). Weir<br />

structures can also be used to replace the need to annually build gravel push up dams. Once<br />

these weir structures are installed and working properly, construction equipment entering and<br />

modifying the channel would no longer be needed prior to the irrigation season. The benefits <strong>of</strong><br />

reducing or eliminating equipment operation during the early spring reduces the possibility <strong>of</strong><br />

crushing salmon redds and young salmonids.<br />

b. Instream Barrier Modification for Fish Passage Improvement<br />

Fish passage improvements will increase access for coho salmon adults and juveniles to<br />

previously unavailable habitat. These restoration activities will likely increase the current spatial<br />

structure <strong>of</strong> coho salmon populations. Reintroducing listed salmonids into previously<br />

unavailable upstream habitat will also likely increase reproductive success and ultimately fish<br />

population size in watersheds where the amount <strong>of</strong> quality freshwater habitat is a limiting factor.<br />

c. Stream Bank Stabilization<br />

In addition to the habitat benefits discussed earlier in the Effects to SONCC Coho Salmon ESU<br />

Critical Habitat section (i.e., section 11.4.2.3), stream bank stabilization will reduce sediment<br />

delivery to the stream and is likely to improve coho salmon embryo and alevin survival in<br />

spawning gravels and reduce injury to juvenile coho salmon from high concentrations <strong>of</strong><br />

suspended sediment. Successfully reducing streambank erosion will be beneficial to coho<br />

salmon because coho salmon will then be exposed to lower suspended sediment concentrations.<br />

365

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