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Bureau of Land Management's Decision Record and Environmental

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Jersey Valley Geothermal Development Project<br />

<strong>Environmental</strong> Assessment: NV063-EAO8-091<br />

Suitable habitat may be present within the surveyed portions <strong>of</strong> the Jersey Valley Unit Area,<br />

however no individuals were observed during the field survey (GBE 2008). Habitat may also be<br />

present along portions <strong>of</strong> the transmission line corridor, however the season long grazing on this<br />

area has reduced the plant diversity over time <strong>and</strong> this species was not observed during the field<br />

survey (GBE 2008).<br />

Reese River Phacelia<br />

Reese River Phacelia habitat is open, dry to moist, alkaline, nearly barren, sometimes scree<br />

covered, whitish to brownish shrink-sell clay soils derived from fluviolacustrine volcanic ash <strong>and</strong><br />

tuff deposits, generally on the steeper slopes <strong>of</strong> low hills, bluffs, <strong>and</strong> badl<strong>and</strong>s in the<br />

shadscale-greasewood, sagebrush, <strong>and</strong> lower pinyon-juniper zones with A triplex confertifolia,<br />

A canescens, Artemisia tridentate, Sarcobatus vermiculatus, tetradym Ia, Phacelia gymnoclada,<br />

Cleomella, etc (NNHP 2001b).<br />

Suitable habitat may be present within the surveyed portions <strong>of</strong> the Jersey Valley Unit Area,<br />

however no species were observed during the field survey (GBE 2008). No Reese River Phacelia<br />

populations were observed along the transmission line corridor (GBE 2008).<br />

Sadaspyrg <strong>and</strong> Dixie Valley pyrg<br />

The Sadas pyrg (Pyrgulopsis sadai) <strong>and</strong> Dixie Valley pyrg (P. dtrensis) are both springsnails<br />

associated with freshwater seeps <strong>and</strong> springs. While the springs occupied by springsnails vary in<br />

their water quality <strong>and</strong> quantity, generally speaking, the springs need to be perennial, have<br />

moderate to high flows, cool temperatures, <strong>and</strong> good water quality. Springs that have been<br />

developed or heavily impacted by livestock, wild horses, or wildlife, are not as likely to have<br />

springsnails as springs with good water quality <strong>and</strong> riparian vegetation (GBE 2008).<br />

The perennial water sources within the Jersey Valley Unit Area consisted <strong>of</strong> two springs, neither<br />

possesses cool water <strong>and</strong> flows were very low. Additionally, both springs were impacted by wild<br />

horses <strong>and</strong> livestock <strong>and</strong> did not appear to be suitable habitat for springsnails. No springsnails<br />

were observed within either spring (GBE 2008). No perennial waters occurred along the<br />

transmission line corridor, <strong>and</strong> therefore, no suitable habitat for the springsnalls existed (GBE<br />

2008).<br />

Western burrowing owl<br />

Western burrowing owls inhabit open terrain <strong>and</strong> typically create a nest by occupying an<br />

ab<strong>and</strong>oned burrow created by other animals such as a badger (Taxidea taxus). They are also<br />

found in roadside berms (Stamm 2006).<br />

Burrowing owl habitat is marginal within the surveyed portions <strong>of</strong> the Jersey Valley Unit Area.<br />

One historically active burrowing owl nest exists within 1 mile <strong>of</strong> the proposed transmission<br />

corridor thus surveys were completed specific to this species. Numerous burrows were observed<br />

during GBE’s 2008 survey, but no sign <strong>of</strong> burrowing owl activity was observed. The survey was<br />

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