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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 />

facilities or downstream sediment transport. Similarly, at sedimentation augmentation<br />

areas downstream of <strong>Middle</strong> <strong>Fork</strong> interbay dam, riparian vegetation management would<br />

occur to ensure that riparian vegetation does not impede downstream transport of<br />

sediment from the augmentation areas. However, under existing conditions, there is<br />

minimal riparian vegetation at these augmentation areas because of steep side slopes,<br />

coarse substrate, and periodic high flows from spills that scour vegetation and prevent<br />

established plant populations.<br />

For routine maintenance activities and non-routine recreation maintenance<br />

activities there may be minor disturbances to existing vegetation. However, vegetation<br />

likely would reestablish through pioneering of plant species from adjacent areas, growth<br />

of plants from the existing seed bank, and restoration of native vegetation as provided for<br />

in the previously discussed VIPMPs.<br />

Effects of Proposed Changes in Hell Hole Reservoir Operations on Vegetation<br />

Daily and seasonal fluctuations in reservoir water surface elevations at <strong>Middle</strong><br />

<strong>Fork</strong> interbay and Ralston afterbay are not expected to change under the proposed action<br />

compared with existing conditions; therefore, riparian resources would be maintained<br />

around these reservoirs. Under the proposed action, average water surface elevation at<br />

French Meadows reservoir in April through August would typically be slightly lower<br />

compared with existing and conditions, and would not likely have a substantive effect on<br />

the associated vegetative communities. However, proposed changes to the operation of<br />

Hell Hole reservoir have the potential to affect plant communities along the shoreline.<br />

Currently, Stebbins’ phacelia grows along the shoreline of Hell Hole reservoir,<br />

including portions of the shoreline that are inundated for part of the growing season<br />

(April through August) in wet, above normal, and below normal water year types (see<br />

table 3.3.1-3). Under the proposed action, in years when French Meadows dam and Hell<br />

Hole dam would spill, operation of Hell Hole reservoir with the proposed modified<br />

spillway crest gates would allow storage of up to an additional 7,600 acre-feet of water.<br />

This operation of the spillway crest gates would result in an increase in the existing<br />

maximum normal operating water surface elevation from 4,630 feet to 4,636 feet in the<br />

early summer. This proposed change in project operations has the potential to affect<br />

Stebbins’ phacelia populations. The Alternative 1 reservoir operating regime, for the<br />

purposes of this analysis, would be essentially the same as the proposed action.<br />

Our Analysis<br />

Changes to spillway crest gate operations could affect Stebbins’ phacelia in Areas<br />

1, 2a, and 2b (table 3.3.3-6). In Area 1, model results for the proposed action indicate<br />

that number of years in which inundation occurs would be similar to existing conditions.<br />

In Area 2a, the overall frequency of inundation during the growing season for Stebbins’<br />

phacelia for all water year types combined would increase from 11 (existing conditions)<br />

to 14 years (proposed operation) over the period of record (33 years modeled). This<br />

increase in inundation frequency would occur in above normal and below normal water<br />

169

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