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EPA's Vessel General Permit and Small Vessel General

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11. Certain park pest management activities (§ 223.203(b)(11))<br />

12. Certain municipal, residential, commercial, <strong>and</strong> industrial development <strong>and</strong><br />

redevelopment activities (§ 223.203(b)(12))<br />

13. Forest management activities on State <strong>and</strong> private l<strong>and</strong>s within the State of Washington<br />

(§ 223.203(b)(13))<br />

14. Activities undertaken consistent with an approved Tribal resource management plan (§<br />

223.204).<br />

Chinook Salmon<br />

Description of the Species<br />

Chinook salmon are the largest of the Pacific salmon <strong>and</strong> historically ranged from the Ventura<br />

River in California to Point Hope, Alaska in North America, <strong>and</strong> in northeastern Asia from<br />

Hokkaido, Japan to the Anadyr River in Russia (Healey 1991). We discuss the distribution,<br />

status, <strong>and</strong> critical habitats of the nine species 3 of endangered <strong>and</strong> threatened Chinook salmon<br />

separately, <strong>and</strong> summarize their common dependence on Waters of the U.S. However, because<br />

listed Chinook salmon species are virtually indistinguishable in the wild <strong>and</strong> comprise the same<br />

biological species, we begin this section describing those characteristics common across ESUs.<br />

Chinook salmon exhibit one of the most varied <strong>and</strong> complex life history strategies. The “streamtype”<br />

of Chinook salmon resides in freshwater for a year or more following emergence <strong>and</strong> the<br />

“ocean-type” migrates to the ocean within their first year. The ocean-type typifies populations<br />

north of 56ºN (Healey 1991). The life cycle of all Chinook salmon spans fresh <strong>and</strong> marine<br />

waters. Spawning migrations generally occur in the spring <strong>and</strong> fall; spawning typically occurs<br />

earlier in the spring/summer at northern latitudes <strong>and</strong> later in southern latitudes (Healey 1991).<br />

Temperature <strong>and</strong> stream flow can significantly influence the timing of migrations <strong>and</strong> spawning,<br />

as well as the selection of spawning habitat (Geist et al. 2009, Hatten <strong>and</strong> Tiffan. 2009). Chinook<br />

salmon are semelparous (i.e. they die after spawning).<br />

While in fresh water, juvenile Chinook salmon are often found in the lower reaches of a river<br />

near its estuary in areas of low water velocity. As they grow, they tend to move to deeper waters<br />

where the velocity is higher (Healey 1991). <strong>General</strong>ly, Chinook salmon outmigrants (smolts) are<br />

about 2 to 5 inches long when they enter saline (often brackish) waters. The process of<br />

smoltification enables salmon to adapt to the ocean environment (Wedemeyer et al. 1980).<br />

Several factors can affect smoltification process, not only at the interface between fresh water<br />

<strong>and</strong> salt water, but higher in the watershed as the process of transformation begins long before<br />

fish enter salt waters. These factors include exposure to chemicals such as heavy metals <strong>and</strong><br />

elevated water temperatures (Wedemeyer et al. 1980).<br />

3 We use the word “species” as it has been defined in section 3 of the ESA, which include “species, subspecies, <strong>and</strong> any distinct<br />

population segment of any species of vertebrate fish or wildlife which interbreeds when mature (16 U.S.C. 1533)”. Pacific<br />

salmon that have been listed as endangered or threatened were listed as “evolutionarily significant units (ESU)” which NMFS<br />

uses to identify distinct population segments (DPS) of Pacific salmon. Any ESU or DPS is a “species” for the purposes of the<br />

ESA.<br />

68

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