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Biological Opinions - Bureau of Reclamation

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Table 8.4 Potential emergent wetland habitat at the Williamson River Delta under different UKL elevations,<br />

based on data in Elseroad (2004) and a GIS analysis <strong>of</strong> topographic data, and assuming no inundation <strong>of</strong><br />

emergent vegetation occurs below 4139.0 ft (1,261.6 m).<br />

UKL<br />

Elevation (ft)<br />

4,143.0<br />

(1,262.8 m)<br />

4,142.0<br />

(1,262.5 m)<br />

4,141.0<br />

(1,262.2 m)<br />

4,140.0<br />

(1,261.9 m)<br />

4,139.0<br />

(1,261.6 m)<br />

Tulana Emergent<br />

Wetland Area (ac)<br />

Goose Bay Emergent<br />

Wetland Area (ac)<br />

Total Williamson River Delta<br />

Emergent Wetland Area (ac)<br />

1,080<br />

1,560<br />

2,640<br />

(437 ha)<br />

(631 ha)<br />

(1,069 ha)<br />

850<br />

1,390<br />

2,240<br />

(344 ha)<br />

(563 ha)<br />

(907 ha)<br />

580<br />

1,080<br />

1,660<br />

(265 ha)<br />

(437 ha)<br />

(672 ha)<br />

290<br />

550<br />

870<br />

(118 ha)<br />

(223 ha)<br />

(352 ha)<br />

0 0 0<br />

At an elevation <strong>of</strong> 4,141.0 ft (1,261.9 m), approximately 1,600 ac (648 ha) <strong>of</strong> the potential<br />

emergent vegetation habitat is available at the Williamson River Delta (Table 8.4). UKL surface<br />

elevations at or above 4,141.0 ft (1,261.9 m) by the end <strong>of</strong> June occurred in one out <strong>of</strong> the 31<br />

modeled years (year 1992; Table 8.1). By the end <strong>of</strong> July, lake levels drop another foot from<br />

June levels (Table 8.5). The amount <strong>of</strong> emergent habitat available at the Williamson River Delta<br />

in UKL declines from 2,640 ac (1,068 ha) at an elevation <strong>of</strong> 4,143.0 ft (1,262.8 m) to 870 ac<br />

(352 ha) at an elevation <strong>of</strong> 4,140.0 ft (1,261.9 m; Table 8.4). At that elevation, any larvae not<br />

present in the wetlands could be more vulnerable to entrainment at the outlet <strong>of</strong> the lake,<br />

predation, and starvation. This would primarily affect SNS larvae because they are more<br />

dependent on wetlands than LRS larvae (Terwilliger 2006; Simon et al. 2010, 2011). At that<br />

elevation substantial larval mortality is likely because <strong>of</strong> the significant reductions in habitat that<br />

would occur. However, elevations below 4,140.0 ft (1,261.9 m) at the end <strong>of</strong> July occurred in<br />

only one year out <strong>of</strong> 31 modeled years (year 1992).<br />

139

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