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Our new Biological Assessment is out - Klamath Basin Crisis

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<strong>Klamath</strong> Project Operations <strong>Biological</strong> <strong>Assessment</strong><br />

Coho Salmon: Effects of the Proposed Action on Coho Salmon<br />

Table 3-27. Total smolt production in year 10 by smolt type for h<strong>is</strong>torical flows (1961 to<br />

2006) and proposed flows (modeled 2008 to 2018) at IGD using 90 percent exceedence<br />

flows combined with 2001 meteorological and tributary flow data, and 50 percent<br />

exceedence flows combined with 2004 data meteorological and tributary flow data<br />

Smolt Type<br />

H<strong>is</strong>torical Flows Proposed Action % Change<br />

(Prop-<br />

Base)<br />

Smolts<br />

produced<br />

% of<br />

total<br />

Smolts<br />

produced<br />

% of<br />

total<br />

Smolts<br />

produced<br />

Type I (tributary) 53,254 84.7% 53,892 84.3% 1.2%<br />

Type II (main stem) 2,216 3.5% 2,344 3.7% 5.8%<br />

Type III (non-natal<br />

tributary)<br />

7,389 11.8% 7,673 12.0% 3.8%<br />

Total 62,859 63,908 1.7%<br />

Type I (tributary) 88,160 86.0% 88,814 86.0% 0.7%<br />

Type II (main stem) 4,362 4.3% 4,497 4.4% 3.1%<br />

Type III (non-natal<br />

tributary)<br />

9,932 9.7% 9,968 9.7% 0.4%<br />

Total 102,454 103,280 0.8%<br />

Another metric used to examine population diversity <strong>is</strong> the percentage of hatchery<br />

f<strong>is</strong>h among f<strong>is</strong>h spawning naturally. The potential certainly ex<strong>is</strong>ts for hatchery<br />

f<strong>is</strong>h to compose a large share of natural spawners, and th<strong>is</strong> appears to be the case<br />

in the Trinity River main stem. Only within the last few years has coho salmon<br />

spawning been surveyed in a number of streams through<strong>out</strong> the basin, and we<br />

have received anecdotal reports that marked hatchery f<strong>is</strong>h were rarely recovered<br />

in tributaries, except in close proximity to the hatchery. Regardless of what<br />

proportion that the hatchery f<strong>is</strong>h compose of spawners in different areas, we are<br />

unaware of evidence anywhere that suggest the operations of IGD will influence<br />

straying of hatchery f<strong>is</strong>h. Accordingly, there <strong>is</strong> no function in the life cycle model<br />

that relates straying to project operations.<br />

Reintroduction of Coho Salmon<br />

Reclamation notes that the in the draft environmental impact statement for the<br />

FERC licensing for the continued operation of PacifiCorp’s <strong>Klamath</strong><br />

Hydroelectric Project, PacifiCorp proposes a suite of studies to be conducted<br />

during Phase 1 of the adaptive salmon reintroduction plan. These studies are<br />

l<strong>is</strong>ted in Table 3-75 of the draft environmental impact statement. Many of the key<br />

uncertainties would be addressed in the first five years of study. Although<br />

PacifiCorp indicates that some aspects of the Phase 1 studies may require 10 years<br />

to complete. PacifiCorp proposes that based on the results and analys<strong>is</strong> of the six<br />

studies, f<strong>is</strong>heries’ managers would decide if self sustaining runs of anadromous<br />

f<strong>is</strong>h can be establ<strong>is</strong>hed (FERC, 2006).<br />

274

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