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EPA's Vessel General Permit and Small Vessel General

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status as threatened on January 5, 2006 (71 FR 834). NMFS 1997 status review identified sharp<br />

declines in the returns of naturally produced steelhead, beginning in the mid-1980s. At the time<br />

nine of 13 trend indicators were in decline <strong>and</strong> the average abundance (geometric mean, 1992-<br />

1996) for the DPS was 75,000 adult steelhead (8,900 naturally produced). Of this, about 7,000<br />

were A-run adults, <strong>and</strong> about 1,400 were B-run adults (Busby et al. 1996).<br />

The lack of data on adult spawning escapement for specific tributaries of the Snake River Basin<br />

DPS continues to make a quantitative assessment of viability difficult. Available data indicate<br />

that the overall long-term estimates of population trends have remained negative (Good et al.<br />

2005). Annual return estimates are limited to counts of the aggregate return over Lower Granite<br />

Dam, <strong>and</strong> spawner estimates for the Tucannon, Asotin, Gr<strong>and</strong>e Ronde <strong>and</strong> Imnaha Rivers. The<br />

2001 return over Lower Granite Dam was substantially higher relative to the low levels seen in<br />

the 1990s; the recent geometric 5-year mean abundance (Total escapement 106,175 with 14,768<br />

natural returns) was approximately 28% of the interim recovery target level (52,000 natural<br />

spawners) (Good et al. 2005). The 10-year average for natural-origin steelhead passing Lower<br />

Granite Dam between 1996 <strong>and</strong> 2005 is 28,303 adults. Long-term trend estimates of the<br />

population growth rate (λ) across the available data set was 0.998 assuming that natural returns<br />

are produced only from natural-origin spawners, <strong>and</strong> 0.733 if both hatchery <strong>and</strong> wild spawners<br />

are contributing to production equally (Good et al. 2005). The Snake River supports<br />

approximately 63% of the total natural-origin production of steelhead in the Columbia River<br />

Basin (Good et al. 2005).<br />

Critical Habitat<br />

NMFS designated critical habitat for Snake River steelhead on September 2, 2005 (70 FR<br />

52630). Designated critical habitat includes the following subbasins: Hells Canyon, Imnaha<br />

River, Lower Snake/Asotin, Upper Gr<strong>and</strong> Ronde River, Wallowa River, Lower Gr<strong>and</strong> Ronde,<br />

Lower Snake/Tucannon, Upper Salmon, Pahsimeroi, Middle Salmon-Panther, Lemhi, Upper<br />

Middle Fork Salmon, Lower Middle Fork Salmon, Middle Salmon, South Fork Salmon, Lower<br />

Salmon, Little Salmon, Upper <strong>and</strong> Lower Selway, Lochsa, Middle <strong>and</strong> South Fork Clearwater,<br />

<strong>and</strong> the Clearwater subbasins, <strong>and</strong> the Lower Snake/Columbia River corridor. These areas are<br />

important for the species’ overall conservation by protecting quality growth, reproduction, <strong>and</strong><br />

feeding. The critical habitat designation for this DPS identifies primary constituent elements that<br />

include sites necessary to support one or more steelhead life stages. Specific sites include<br />

freshwater spawning sites, freshwater rearing sites, freshwater migration corridors, nearshore<br />

marine habitat <strong>and</strong> estuarine areas. The physical or biological features that characterize these<br />

sites include water quality <strong>and</strong> quantity, natural cover, forage, adequate passage conditions, <strong>and</strong><br />

floodplain connectivity. The final rule (70 FR 52630) lists the watersheds that comprise the<br />

designated subbasins <strong>and</strong> any areas that are specifically excluded from the designation.<br />

There are 289 watersheds within the range of Snake River steelhead. The total area of habitat<br />

designated as critical includes about 8,000 miles of stream habitat. This designation includes the<br />

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

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

lateral extent is defined as the bankfull elevation. Of the 289 fifth order streams reviewed in this<br />

DPS, 231 received a high conservation value rating, 44 received a medium rating <strong>and</strong> 14<br />

received a rating of low conservation value for the species. The lower Snake/Columbia<br />

118

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