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Biological Opinions - Bureau of Reclamation

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Threat<br />

Nature <strong>of</strong><br />

Threat<br />

Life Stage<br />

Affected<br />

age-0<br />

Primary Effect<br />

Mitigating<br />

Factor(s)<br />

documented<br />

especially at<br />

population<br />

level, but birds<br />

are known<br />

predators<br />

References<br />

2007, Roby<br />

and Collis<br />

2011<br />

7.10.5 Effects <strong>of</strong> Ecosystem Restoration and Recovery Actions for the LRS and the<br />

SNS<br />

Since the early 1990s, the USFWS, <strong>Reclamation</strong>, NRCS, the State <strong>of</strong> Oregon, the Klamath<br />

Tribes, The Nature Conservancy, Klamath water users, other partners, and private landowners<br />

have been working to improve water quality and aquatic habitat conditions in the upper Klamath<br />

River Basin to support the recovery <strong>of</strong> the LRS and the SNS. Major habitat restoration efforts<br />

focusing on the endangered suckers have been completed or initiated. These include: (1)<br />

enhancement <strong>of</strong> thousands <strong>of</strong> acres <strong>of</strong> wetlands adjacent to UKL and in the watershed above the<br />

lake; (2) removal <strong>of</strong> Chiloquin Dam; (3) screening <strong>of</strong> the outlet <strong>of</strong> Clear Lake Dam; (4)<br />

construction <strong>of</strong> a new fish ladder at Link River Dam; and (5) screening <strong>of</strong> the A Canal.<br />

7.10.5.1 Wetland Restoration in UKL<br />

The re-establishment <strong>of</strong> approximately 2,600 ac (1,050 ha) <strong>of</strong> shallow water habitat at the<br />

Williamson River Delta, which is likely to be become emergent marsh (Elseroad 2004), is<br />

expected to provide good habitat for larval suckers, and will perhaps increase survivorship and<br />

reduce vagrancy and dispersal out <strong>of</strong> UKL where survival is currently minimal (Crandall et al.<br />

2008; Hendrixson 2008; Markle et al. 2009; Erdman et al. 2010, 2011). Monitoring has shown<br />

that larval suckers are extensively using a variety <strong>of</strong> microhabitats in the newly reconnected<br />

wetlands; they have a greater gut-fullness, and in some years are larger, than larvae in the lake<br />

(Crandall et al. 2008; Erdman and Hendrixson 2010, 2011). Additionally, restoration at the<br />

Williamson River Delta altered the path water takes when it reaches the lake, which appears to<br />

have affected the distribution <strong>of</strong> larvae, making it less likely they will be transported out <strong>of</strong> the<br />

lake (Simon et al. 2012). On the potentially negative side: in some years habitat used by larval<br />

suckers becomes dewatered by mid-July; a large number <strong>of</strong> nonnative fish, including six species<br />

that could prey on larval suckers and three that could prey on juveniles, occur in the Williamson<br />

River Delta; catch rates <strong>of</strong> age-0 suckers decline to near zero by September; and water quality in<br />

areas with deep-water emergent and transitional wetlands is poor in late summer (TNC 2009,<br />

Burdick 2012, Burdick and Hewitt 2012). Additionally, wetland habitats in the Delta provide<br />

habitat for snails that could be one source <strong>of</strong> parasitic trematodes now infecting juvenile suckers.<br />

Agency Lake Ranch and the Barnes properties (9,800 ac [4,000 ha]) along the northern and<br />

northwestern shores <strong>of</strong> Agency Lake were acquired by <strong>Reclamation</strong> and used as water storage<br />

areas, but are now managed as a part <strong>of</strong> the Upper Klamath NWR. Levees along these properties<br />

could be breached within the next 10 years; however, because <strong>of</strong> subsidence, much <strong>of</strong> the<br />

property will be too deep to maintain emergent wetland vegetation used by young suckers and<br />

100

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