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Biological Opinions - Bureau of Reclamation

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8.3.7.4 Effects <strong>of</strong> Entrainment Losses <strong>of</strong> SNS at Gerber Reservoir<br />

Past efforts to quantify entrainment or salvage-stranded suckers in Miller Creek downstream<br />

from Gerber Dam as a result <strong>of</strong> Project operations suggest that several hundred age-0 and older<br />

juvenile suckers are annually entrained at the dam as result <strong>of</strong> Project operations (Hamilton et al.<br />

2003). Based on the quantities <strong>of</strong> water delivered in the past decade and the proposed action,<br />

<strong>Reclamation</strong> assumed several hundred age-0 and older juvenile suckers will be annually<br />

entrained under the proposed action (USBR 2012). Larval and age-0 juvenile suckers are also<br />

likely entrained, but this has not been studied.<br />

The proposed action includes opening <strong>of</strong> Gerber Dam frost valves at the end <strong>of</strong> the irrigation<br />

season that, which allows for a flow <strong>of</strong> approximately 5 cfs (0.1 m 3 /sec) in Miller Creek.<br />

Downstream accretions from seeps and storm run<strong>of</strong>f increase the actual instream flow within<br />

Miller Creek. This flow may still not be sufficient to allow for stream pool connectivity (USBR<br />

2012) and consequently some suckers are likely to be stranded stream pools and die at the end <strong>of</strong><br />

the irrigation season.<br />

There is likely to be entrainment losses <strong>of</strong> larval, juvenile and adult suckers as a result <strong>of</strong> the<br />

proposed action at Gerber Reservoir. However, available information (Barry et al. 2009, 2007a,<br />

Leeseberg et al. 2007) indicates that the Gerber Reservoir SNS population has remained<br />

moderately large and has frequent recruitment under the current management regime, and so we<br />

anticipate this will continue under the proposed action. Thus, levels <strong>of</strong> entrainment that are<br />

likely to occur with implementation <strong>of</strong> the proposed action and the resulting adverse effects to<br />

SNS are unlikely to occur at a level that limits the persistence <strong>of</strong> SNS in Gerber Reservoir.<br />

Summary <strong>of</strong> Effects to LRSs and SNSs in the Gerber Reservoir<br />

Based on the analysis presented above, the USFWS concludes that most <strong>of</strong> the biological effects<br />

<strong>of</strong> the proposed action to SNS in Gerber Reservoir are likely to be compatible with the<br />

conservation needs <strong>of</strong> the SNS. Entrainment is likely to be the most significant adverse effect,<br />

but because the SNS population has remained viable with current levels <strong>of</strong> entrainment, and<br />

operations is not anticipated to change, adverse effects are unlikely to occur at a level that limits<br />

the persistence <strong>of</strong> SNS in Geber Reservoir.<br />

8.3.8 Effects to the LRS and the SNS in Tule Lake Sump 1A<br />

Tule Lake consists <strong>of</strong> two sumps: Sump 1A (9,000 ac [3,642 ha]) and Sump 1B (4,000 ac [1,619<br />

ha]). There is a small population <strong>of</strong> the LRS and the SNS located in Sump 1A. Only, a few<br />

suckers have ever been documented in Sump 1B, despite the fact that there is access to Sump 1B<br />

from 1A (Freitas et al. 2007). It is unknown why suckers do not inhabit Sump 1B, but in an<br />

effort to better understand this situation, 18 radio-tagged suckers were experimentally put into<br />

Sump 1B in 2011 to assess their movements and survival. All, <strong>of</strong> these suckers returned to Sump<br />

1A when access became available in 2012, confirming that, for unknown reasons, suckers prefer<br />

Sump 1A.<br />

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