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Biological Opinions - Bureau of Reclamation

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much as 40 to 60 percent, suggesting a lack <strong>of</strong> resiliency. SNSs in UKL are also vulnerable<br />

because most are well past their average life expectancy, and LRSs are at their average life<br />

expectancy, thus the rate <strong>of</strong> decline could increase if there is not substantial recruitment into the<br />

adult age class. However, recruitment <strong>of</strong> both species into the adult population in UKL in the<br />

past decade has been nearly nonexistent, and there is no evidence <strong>of</strong> large cohorts <strong>of</strong> young<br />

suckers that could enter the adult population in the next few years. Loss <strong>of</strong> the UKL populations<br />

would leave only one self-sustaining population <strong>of</strong> the LRS and two populations <strong>of</strong> the SNS;<br />

thus, there is little redundancy for either species, adding to their risk <strong>of</strong> extinction. Given this<br />

information, the Service finds that LRS and SNS populations, especially the SNS population in<br />

UKL, are at a high risk <strong>of</strong> extinction.<br />

7.6 Survival and Recovery Needs <strong>of</strong> the LRS and the SNS<br />

The 2013 revised recovery plan for the LRS and SNS (USFWS 2013) describes their survival<br />

and recovery needs, which are:<br />

<br />

<br />

Adequate quality and quantity <strong>of</strong> habitat to support the needs <strong>of</strong> all life stages <strong>of</strong> LRS and<br />

SNS.<br />

o Improved water quality to a level where adverse effects are not sufficient to<br />

threaten the continued persistence <strong>of</strong> the LRS and the SNS.<br />

o Connectivity throughout the range <strong>of</strong> LRS and SNS to ensure appropriate genetic<br />

exchange among populations, to provide access to spawning and refugial areas,<br />

and to permit return <strong>of</strong> downstream migrants.<br />

A sufficient number <strong>of</strong> viable, self-sustaining populations <strong>of</strong> the LRS and SNS to buffer<br />

against localized extirpations.<br />

o Substantially reduced entrainment <strong>of</strong> larval, juvenile and adult LRS and SNS<br />

particularly in UKL.<br />

o Increased frequency and magnitude <strong>of</strong> recruitment into the adult spawning<br />

populations <strong>of</strong> both the LRS and the SNS.<br />

o Populations <strong>of</strong> sufficient sizes to ensure genetic variability to enable LRS and<br />

SNS to respond to changing ecosystem conditions.<br />

7.7 <strong>Reclamation</strong>’s Klamath Project<br />

7.7.1 Hydrologic Alteration<br />

The <strong>Reclamation</strong> Act <strong>of</strong> 1902 (43 U.S.C. 391 et seq.) authorized the Secretary <strong>of</strong> the Interior to<br />

locate, construct, operate, and maintain works for the storage, diversion, and development <strong>of</strong><br />

water for the reclamation <strong>of</strong> arid and semiarid lands in the western States. Congress facilitated<br />

development <strong>of</strong> the Klamath Project by authorizing the Secretary to raise or lower the level <strong>of</strong><br />

Lower Klamath and Tule Lakes and to dispose <strong>of</strong> the land uncovered by such operation for use<br />

under the <strong>Reclamation</strong> Act <strong>of</strong> 1902. The Oregon and California legislatures passed legislation<br />

for certain aspects <strong>of</strong> the Klamath Project, and the Secretary <strong>of</strong> the Interior authorized<br />

construction May 15, 1905, in accordance with the <strong>Reclamation</strong> Act <strong>of</strong> 1902 (Act <strong>of</strong> February 9,<br />

61

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