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Biological Opinions - Bureau of Reclamation

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action. <strong>Reclamation</strong> estimated that the proposed action would result in flows that could support<br />

over 20,000 coho salmon in the mainstem Klamath River in the R Ranch and Trees <strong>of</strong> Heaven<br />

reaches. Assuming 50 coho salmon redds in the mainstem Klamath River, <strong>Reclamation</strong><br />

estimated that 9,000 natural origin coho salmon juveniles resulting from mainstem spawning<br />

may be present in the mainstem. Based on the available habitat, <strong>Reclamation</strong> concluded that the<br />

proposed action will likely provide adequate habitat for natural-origin juvenile coho salmon<br />

during the spring until the annual hatchery goal <strong>of</strong> 75,000 IGH coho salmon juveniles are<br />

released into the mainstem Klamath River between March 15 and May 1 (CDFG 2012 in<br />

<strong>Reclamation</strong> 2012). Although <strong>Reclamation</strong> (2012) did not analyze competition or predation by<br />

hatchery-origin or natural-origin Chinook salmon and steelhead, <strong>Reclamation</strong> (2012)<br />

acknowledged that coho salmon juveniles rearing in the mainstem will experience decreased<br />

growth, increased or premature emigration, increased competition for food, decreased feeding<br />

territory sizes, and increased mortalities following the release <strong>of</strong> approximately 75,000 hatcheryorigin<br />

coho salmon.<br />

NMFS concurs with <strong>Reclamation</strong>’s assessment that habitat availability for juveniles in the<br />

mainstem Klamath River is most critical between March to June because <strong>of</strong>: (1) the spring<br />

redistribution <strong>of</strong> coho salmon parr; (2) the presence <strong>of</strong> most, if not all, coho salmon smolts from<br />

the Interior Klamath Diversity Stratum in the mainstem during this time; and (3) the presence <strong>of</strong><br />

other stressors, such as the addition <strong>of</strong> IGH salmonids, the onset <strong>of</strong> elevated water temperatures,<br />

and disease prevalence. During the spring, natural origin coho salmon parr and, to a lesser<br />

extent, smolts compete for habitat with natural origin and hatchery-released salmon and<br />

steelhead in late March to June. Competition for habitat peaks during May and early June when<br />

natural origin smolts co-occur with approximately five million Chinook salmon smolts from<br />

IGH. Therefore, habitat availability during spring is the most essential for coho salmon<br />

juveniles.<br />

During the fall (i.e., October and November), coho salmon parr migrate through mainstem<br />

habitat as they redistribute from thermally suitable, summer habitat into winter rearing habitat<br />

characterized by complex habitat structure and low water velocities in tributaries (Lestelle 2007).<br />

The presence <strong>of</strong> coho salmon juveniles in the mainstem Klamath River is likely low in the fall<br />

and winter, and habitat availability in the mainstem Klamath River during the fall and winter is<br />

not considered limited. During the summer, coho salmon juveniles in the mainstem are limited<br />

to thermal refugia during the day, and habitat availability in the mainstem Klamath River during<br />

the summer is not considered limited for the relatively fewer coho salmon parr rearing in the<br />

mainstem during this period.<br />

The amount <strong>of</strong> rearing habitat available in the mainstem Klamath River is correlated with flows,<br />

especially at certain ranges where water velocity, depth, and cover provide suitable conditions<br />

for fry and juvenile rearing (Figures 11.17 and 11.18). As discussed earlier in the Effects to<br />

SONCC Coho Salmon ESU Critical Habitat section, the Trees <strong>of</strong> Heaven, Seiad Valley, and<br />

Rogers Creek reaches all show reduced habitat availability as a result <strong>of</strong> the proposed action.<br />

Further downstream at the Rogers Creek reach, the proposed action will reduce habitat<br />

availability between March and June in average water years (≥50 percent exceedance; Table<br />

11.12) and in above average water years for the latter spring months (Table 11.12).<br />

352

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