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Draft EIS_072312.pdf - Middle Fork American River Project ...

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20120723-4002 FERC PDF (Unofficial) 07/23/2012<br />

Our Analysis<br />

Although some riparian habitat would be removed as a result of the proposed and<br />

Alternative 1 actions, we find that increased minimum instream flows, pulse flows with<br />

recession rates (in the bypassed reaches only), and down-ramping of spills below French<br />

Meadows and Hell Hole reservoir would enhance riparian resources along 79 miles of<br />

bypassed reaches and would maintain riparian resources along 28 miles along the peaking<br />

reach. In addition, implementation of minimum reservoir pool requirements, installation<br />

of the Hell Hole spillway gates, and small diversion modifications would maintain<br />

riparian resources at project reservoirs and diversion pools. Implementing measures<br />

incorporated in the Alternative 1 VIPMP, which include vegetation removal outside of<br />

the bird breeding season, would protect nesting birds using riparian habitat, including<br />

species protected by the Migratory Bird Treaty Act and reduce the risk of effects on other<br />

breeding special-status species, should they occur in riparian habitat. Although the bird<br />

breeding season does not completely encompass the maternity season for bats, the<br />

riparian-roosting western red bat is not a colonial nester; therefore, it is unlikely that a<br />

large roost would be disturbed.<br />

Aquatic Dependent Wildlife<br />

Proposed actions may affect wildlife species that either forage or breed along or<br />

near aquatic habitat. <strong>Project</strong> actions that have the potential to affect aquatic dependent<br />

wildlife (such as invertebrate or fish that provide a prey base for special-status wildlife)<br />

include use of pesticides as part of routine vegetation and noxious weed management,<br />

fluctuation of water elevations at small and medium diversions, increasing instream flows<br />

in the bypassed and peaking reaches, reducing flow fluctuations in the peaking reach,<br />

changing reservoir volume, modification of diversion pools, and continued stocking of<br />

fish in French Meadows and Hell Hole reservoirs. In addition to foothill yellow-legged<br />

frog, western pond turtle, bald eagle, and osprey (discussed previously), other specialstatus<br />

bird species and mammals have been documented foraging at project-affected<br />

streams and reservoirs (e.g., <strong>American</strong> white pelican, Vaux’s swift, pallid bat,<br />

Townsend’s big-eared bat, and western red bat) and could potentially breed near project<br />

waterbodies (e.g., harlequin duck).<br />

PCWA’s proposed and Alternative 1 sediment management activities and<br />

modification of minimum instream flows, spill flows, and pulse flows are described<br />

previously in this section in the discussion of the foothill yellow-legged frog and in more<br />

detail in sections 3.3.1.2, Geologic and Soils Resources, and 3.3.2.2, Aquatic Resources.<br />

Fluctuation of impoundment water surface elevations as a result of sediment management<br />

activities is described previously in the discussion of the western pond turtle. PCWA’s<br />

proposed and the Alternative 1 VIPMPs are discussed in detail in section 3.3.3.2.1,<br />

Vegetation.<br />

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