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EPA's Vessel General Permit and Small Vessel General

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Critical Habitat<br />

NMFS designated critical habitat for Snake River spring/summer-run Chinook salmon on<br />

October 25, 1999 (64 FR 57399). This critical habitat encompasses the waters, waterway<br />

bottoms, <strong>and</strong> adjacent riparian zones of specified lakes <strong>and</strong> river reaches in the Columbia River<br />

that are or were accessible to listed Snake River salmon (except reaches above impassable<br />

natural falls, <strong>and</strong> Dworshak <strong>and</strong> Hells Canyon Dams). Adjacent riparian zones are defined as<br />

those areas within a horizontal distance of 300 feet from the normal line of high water of a<br />

stream channel or from the shoreline of a st<strong>and</strong>ing body of water. Designated critical habitat<br />

includes the Columbia River from a straight line connecting the west end of the Clatsop jetty<br />

(Oregon side) <strong>and</strong> the west end of the Peacock jetty (Washington side) <strong>and</strong> including all river<br />

reaches from the estuary upstream to the confluence of the Snake River, <strong>and</strong> all Snake River<br />

reaches upstream to Hells Canyon Dam; the Palouse River from its confluence with the Snake<br />

River upstream to Palouse Falls, the Clearwater River from its confluence with the Snake River<br />

upstream to its confluence with Lolo Creek; the North Fork Clearwater River from its confluence<br />

with the Clearwater river upstream to Dworshak Dam. Critical habitat also includes several river<br />

reaches presently or historically accessible to Snake River spring/summer Chinook salmon.<br />

These areas are important for the species’ overall conservation by protecting quality growth,<br />

reproduction, <strong>and</strong> feeding. Limiting factors identified for this species include hydrosystem<br />

mortality, reduced stream flow, altered channel morphology <strong>and</strong> floodplain, excessive fine<br />

sediment, <strong>and</strong> degraded water quality (NMFS 2006d).<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 Snake River spring/summer-run Chinook salmon ESU.<br />

Upper Willamette River Chinook Salmon<br />

Distribution <strong>and</strong> Description of the Listed Species<br />

The Upper Willamette River Chinook salmon ESU includes all naturally spawned populations of<br />

spring-run Chinook salmon in the Clackamas River <strong>and</strong> in the Willamette River, <strong>and</strong> its<br />

tributaries, above Willamette Falls, Oregon. Seven artificial propagation programs are part of<br />

the ESU.<br />

Upper Willamette River Chinook salmon occupy the Willamette River <strong>and</strong> its tributaries. All<br />

spring-run Chinook salmon in the ESU, except those entering the Clackamas River, must pass<br />

Willamette Falls. In the past, this ESU included sizable numbers of spawning salmon in the<br />

Santiam River, the middle fork of the Willamette River, <strong>and</strong> the McKenzie River, as well as<br />

smaller numbers in the Molalla River, Calapooia River <strong>and</strong> Albiqua Creek. Historically, access<br />

above Willamette Falls was restricted to the spring when flows were high. In autumn, low flows<br />

84

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