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EPA's Vessel General Permit and Small Vessel General

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made at this time, includes the stream channels within the designated stream reaches, <strong>and</strong><br />

includes a lateral extent as defined by the ordinary high water line. In areas where the ordinary<br />

high-water line is not defined, the lateral extent is defined as the bankfull elevation.<br />

The specific primary constituent elements identified for Hood Canal summer-run chum salmon<br />

are areas for spawning, freshwater rearing <strong>and</strong> migration, estuarine areas free of obstruction,<br />

nearshore marine areas free of obstructions, <strong>and</strong> offshore marine areas with good water quality.<br />

The physical or biological features that characterize these sites include water quality <strong>and</strong><br />

quantity, natural cover, forage, adequate passage conditions, <strong>and</strong> floodplain connectivity. Of 17<br />

subbasins reviewed in NMFS' assessment of critical habitat for the Hood Canal chum salmon<br />

ESU, 14 subbasins were rated as having a high conservation value, while only three were rated<br />

as having a medium value to conservation. These areas are important for the species’ overall<br />

conservation by protecting quality growth, reproduction, <strong>and</strong> feeding. Limiting factors identified<br />

for this species include degraded floodplain <strong>and</strong> mainstem river channel structure, degraded<br />

estuarine conditions <strong>and</strong> loss of estuarine habitat, riparian area degradation <strong>and</strong> loss of in-river<br />

wood in mainstem, excessive sediment in spawning gravels, <strong>and</strong> reduced stream flow in<br />

migration areas.<br />

Final Protective Regulations<br />

On June 28, 2005, as part of the final listing determinations for 16 ESUs of West Coast salmon,<br />

NMFS amended <strong>and</strong> streamlined the 4(d) protective regulations for threatened salmon <strong>and</strong><br />

steelhead (70 FR 37160) as described in the Protective Regulations for Threatened Salmonid<br />

Species section of this document. Under this change, the section 4(d) protections apply to<br />

natural <strong>and</strong> hatchery fish with an intact adipose fin, but not to listed hatchery fish that have had<br />

their adipose fin removed prior to release into the wild. The amended June 2005 4(d) rule<br />

applies to the Hood Canal summer-run chum salmon ESU.<br />

Coho Salmon<br />

Description of the Species<br />

Coho salmon occur naturally in most major river basins around the North Pacific Ocean from<br />

central California to northern Japan (Laufle et al. 1986). They spawn in the fall <strong>and</strong> winter <strong>and</strong><br />

the young emerge in the spring. Adult coho salmon may remain in fresh water three or more<br />

months before spawning, with early migrants often moving farther upstream than later migrants<br />

(S<strong>and</strong>ercock 1991). Spawning occurs in a few third-order streams, but most spawning activity<br />

occurs in fourth- <strong>and</strong> fifth-order streams. As with other Pacific salmon, coho salmon fecundity<br />

varies with the size of the fish <strong>and</strong> latitudinally with coho salmon in northern climes generally<br />

exhibiting higher rates of fecundity (S<strong>and</strong>ercock 1991). Most coho salmon mature <strong>and</strong> spawn at<br />

age 3, although there are exceptions (S<strong>and</strong>ercock 1991).<br />

The outmigration of coho smolts begins as early as February <strong>and</strong> may continue through the<br />

summer <strong>and</strong> fall, with peak outmigration often between March <strong>and</strong> June, although this varies<br />

among basins <strong>and</strong> environmental conditions (S<strong>and</strong>ercock 1991). While at sea, coho salmon tend<br />

to eat fish including herring, s<strong>and</strong> lance, sticklebacks, sardines, shrimp <strong>and</strong> surf smelt. While in<br />

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