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EPA's Vessel General Permit and Small Vessel General

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support one or more Chinook salmon life stages. Specific sites include freshwater spawning<br />

sites, freshwater rearing sites, freshwater migration corridors, nearshore marine habitat <strong>and</strong><br />

estuarine areas. The physical or biological features that characterize these sites include water<br />

quality <strong>and</strong> quantity, natural cover, forage, adequate passage conditions, <strong>and</strong> floodplain<br />

connectivity. The critical habitat designation (70 FR 52488) contains additional details on the<br />

sub-areas that are included as part of this designation, <strong>and</strong> the areas that were excluded from<br />

designation.<br />

In total, California Coastal Chinook salmon occupy 45 watersheds (freshwater <strong>and</strong> estuarine).<br />

The total area of habitat designated as critical includes about 1,500 miles of stream habitat <strong>and</strong><br />

about 25 square miles of estuarine habitat, mostly within Humboldt Bay. This designation<br />

includes the stream channels within the designated stream reaches, <strong>and</strong> includes a lateral extent<br />

as defined by the ordinary high water line. In areas where the ordinary high-water line is not<br />

defined the lateral extent is defined as the bankfull elevation. In estuarine areas the lateral extent<br />

is defined by the extreme high water because extreme high tide areas encompass those areas<br />

typically inundated by water <strong>and</strong> regularly occupied by juvenile salmon during the spring <strong>and</strong><br />

summer, when they are migrating in the nearshore zone <strong>and</strong> relying on cover <strong>and</strong> refuge qualities<br />

provided by these habitats, <strong>and</strong> while they are foraging. Of the 45 watershed reviewed in NMFS'<br />

assessment of critical habitat for California Coastal Chinook salmon, eight watersheds received a<br />

low rating of conservation value, 10 received a medium rating, <strong>and</strong> 27 received a high rating of<br />

conservation value for the species.<br />

Critical habitat in this ESU consists of limited quantity <strong>and</strong> quality summer <strong>and</strong> winter rearing<br />

habitat, as well as marginal spawning habitat. Compared to historical conditions, there are fewer<br />

pools, limited cover, <strong>and</strong> reduced habitat complexity. The limited instream cover that does exist<br />

is provided mainly by large cobble <strong>and</strong> overhanging vegetation. Instream large woody debris,<br />

needed for foraging sites, cover <strong>and</strong> velocity refuges is especially lacking in most of the streams<br />

throughout the basin. NMFS has determined that these degraded habitat conditions are, in part,<br />

the result of many human-induced factors including dam construction, agricultural <strong>and</strong> mining<br />

activities, urbanization, stream channelization, water diversion <strong>and</strong> logging.<br />

Central Valley Spring-Run Chinook Salmon<br />

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

The Central Valley spring-run Chinook salmon ESU includes all naturally spawned populations<br />

of spring-run Chinook salmon in the Sacramento River <strong>and</strong> its tributaries in California. This<br />

ESU includes one artificial propagation program. Central Valley spring-run Chinook salmon<br />

ESU includes Chinook salmon entering the Sacramento River from March to July <strong>and</strong> spawning<br />

from late August through early October, with a peak in September. Spring-run fish in the<br />

Sacramento River exhibit an ocean-type life history, emigrating as fry, sub-yearlings <strong>and</strong><br />

yearlings. Central Valley spring-run Chinook salmon require cool freshwater while they mature<br />

over the summer.<br />

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

NMFS originally listed Central Valley spring-run Chinook salmon as threatened on September<br />

16, 1999 (64 FR 50393), a classification this species retained on June 28, 2005 (70 FR 37160).<br />

72

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