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EPA's Vessel General Permit and Small Vessel General

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earing/migration corridor downstream of the spawning range has a high conservation value.<br />

Limiting factors identified for Snake River Basin steelhead include: hydrosystem mortality,<br />

reduced stream flow, altered channel morphology <strong>and</strong> floodplain, excessive sediment, degraded<br />

water quality, harvest impacts, <strong>and</strong> hatchery impacts.<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) (70 FR<br />

37160) rule applies to the Snake River Basin steelhead DPS.<br />

South-Central California Coast Steelhead<br />

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

The South-Central California Coast steelhead DPS includes all naturally spawned populations of<br />

steelhead (<strong>and</strong> their progeny) in streams from the Pajaro River (inclusive) to, but not including<br />

the Santa Maria River, California. No artificially propagated steelhead populations that reside<br />

within the historical geographic range of this DPS are included in this designation. The two<br />

largest basins within this DPS are the inl<strong>and</strong> basins of the Pajaro River <strong>and</strong> the Salinas River.<br />

Both of these watersheds drain intercoastal mountain ranges <strong>and</strong> have long alluvial lower<br />

stretches. Principle sub-basins in the Pajaro River that support steelhead include: Corralitos<br />

Creek, Pescadero Creek, Uvas Creek <strong>and</strong> Pacheco Creek. Principle sub-basins in the Salinas<br />

River that support steelhead include the Arroyo Seco River, Gabilan Creek, Paso Robles Creek,<br />

Atascadero Creek <strong>and</strong> Santa Margarita Creek. Other important watersheds include the smaller<br />

coastal basins of the Carmel River, <strong>and</strong> St. Rosa <strong>and</strong> San Luis Obispos creeks.<br />

Status <strong>and</strong> Trends<br />

NMFS listed South-Central California Coast steelhead as threatened in 1997, <strong>and</strong> reaffirmed<br />

their status as threatened on January 5, 2006 (71 FR 834). Historical data on the South-Central<br />

California Coast steelhead DPS are sparse <strong>and</strong> no credible historic or recent estimates of total<br />

DPS size are available. Steelhead are present in a large portion of the historically occupied<br />

basins within this DPS (estimated 86-95 %) but observed <strong>and</strong> inferred abundance suggest many<br />

of this basins support a small fragment of their historic run size. Present population trends<br />

within individual watersheds continuing to support runs is generally unknown, but may vary<br />

widely between watersheds. No data are available to estimate the steelhead abundance or trends<br />

in the two largest watersheds in the DPS, the Pajaro <strong>and</strong> Salinas basins. These basins are highly<br />

degraded <strong>and</strong> expected to support runs much reduced in size from historical levels.<br />

Steelhead in the Carmel Basin have been monitored at San Clemente Dam since 1964,<br />

representing one of the longest data sets available for steelhead in this DPS. However, this data<br />

is also limited because a nine year gap exists in the series, a large portion of the run spawns<br />

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