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Biological Opinions - Bureau of Reclamation

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consists <strong>of</strong> approximately 29,000 acres <strong>of</strong> irrigated land with an estimated annual irrigation<br />

withdrawal <strong>of</strong> approximately 81,070 acre feet per year (Van Kirk and Naman 2008).<br />

Agricultural diversions in both the Shasta and Scott rivers in some years, especially dry water<br />

years, can virtually dewater sections <strong>of</strong> these rivers, impacting coho salmon within these streams<br />

as well as those in the Klamath River.<br />

There are two other diversion systems within the Klamath River Basin that affect the action area<br />

for purposes <strong>of</strong> NMFS’ BiOp. Fourmile Creek and Jenny Creek diversions transfer water from<br />

the Klamath River Basin into the Rogue River Basin. Estimated annual (1960 to 1996) out <strong>of</strong><br />

basin diversions from the Fourmile Creek drainage <strong>of</strong> the Klamath River basin to the Rogue<br />

River Basin was approximately 4,845 acre-feet. Net out <strong>of</strong> basin diversions from the Jenny<br />

Creek drainage <strong>of</strong> the Klamath River Basin to the Rogue River Basin were approximately 22,128<br />

acre-feet (38,620 acre-feet exported - 16,492 acre-feet imported). Thus the total average annual<br />

(1960 to 1996) diversions from the Klamath River Basin to the Rogue River Basin was 26,973<br />

acre-feet (La Marche 2001).<br />

As the value <strong>of</strong> farm lands increased throughout the Klamath River Basin, flood control<br />

measures were implemented. During the 1930s, the U.S. Army Corps <strong>of</strong> Engineers implemented<br />

flood control measures in the Scott River Valley by removing riparian vegetation and building<br />

dikes to constrain the stream channel. As a result <strong>of</strong> building these dykes (banking), the river<br />

became more channeled, water velocities increased, and the rate <strong>of</strong> bank erosion accelerated. To<br />

minimize damage, the Soil Conservation Service (now known as NRCS) in Siskiyou County<br />

planted willows along the stream-bank and recommended channel modifications take place<br />

which re-shaped the stream channel into a series <strong>of</strong> gentle curves. The effectiveness <strong>of</strong> these<br />

actions has not yet been measured.<br />

There has been a recent decline in UKL outflows since the 1960s, which is likely due to<br />

increasing diversions, decreasing net inflows, or other factors (Mayer 2008). There have been<br />

declines in winter precipitation in the upper Klamath Basin in recent decades and declines in<br />

upper-Klamath Lake inflow and tributary inflow, particularly base flows (Mayer 2008).<br />

Declines in tributary base flow could be due to increase consumptive use, in particular,<br />

groundwater use, and/or climate changes. Agricultural diversions from the lake have increased<br />

over the 1961 to 2007 period, particularly during dry years (Mayer 2008). Declines in Link<br />

River flows and Klamath River at Keno flows in the last 40-50 years have been most pronounced<br />

during the base flow season (Mayer 2008), the time when agricultural demands are the greatest.<br />

Consumptive use <strong>of</strong> water is expected to negatively impact one or more <strong>of</strong> the VSP criteria for<br />

the interior Klamath populations because it reduces summer and fall discharge <strong>of</strong> tributaries that<br />

the populations use (Van Kirk and Naman 2008); and low flows in the summer have been cited<br />

as limiting coho salmon survival in the Klamath Basin (CDFG 2002a; NRC 2004). Specifically,<br />

the spatial structure, population abundance, and productivity can be impacted by agricultural<br />

activities. Altered flows likely interfere with environmental cues that initiate distribution <strong>of</strong><br />

juvenile coho salmon in the river, alter seaward migration timing, and potentially impact other<br />

important ecological functions, leaving juveniles exposed to a range <strong>of</strong> poor quality habitat, and<br />

prolonged exposure to stressful over wintering and summer rearing conditions (NMFS 2010a).<br />

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