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Carbaryl, Carbofuran, and Methomyl - National Marine Fisheries ...

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limited to a very restricted portion of the historical range. Significant spawning occurs in<br />

only two of the 16 historical populations. Nearly 88% of the historical populations are<br />

extirpated. The two remaining populations are the Grays River <strong>and</strong> the Lower Gorge<br />

(Good, Waples et al. 2005). Chum salmon appear to be extirpated from the Oregon<br />

portion of this ESU. In 2000, the Oregon Department of Fish <strong>and</strong> Wildlife (ODFW)<br />

conducted surveys to determine the abundance <strong>and</strong> distribution of chum salmon in the<br />

Columbia River. Of 30 sites surveyed, only one chum salmon was observed.<br />

Historically, the Columbia River chum salmon supported a large commercial fishery in<br />

the first half of this century which l<strong>and</strong>ed more than 500,000 fish per year as recently as<br />

1942. Commercial catches declined beginning in the mid-1950s, <strong>and</strong> in later years rarely<br />

exceeded 2,000 per year. During the 1980s <strong>and</strong> 1990s, the combined abundance of<br />

natural spawners for the Lower Gorge, Washougal, <strong>and</strong> Grays River populations was<br />

below 4,000 adults. In 2002, however, the abundance of natural spawners exhibited a<br />

substantial increase at several locations (estimate of natural spawners is approximately<br />

20,000 adults). The cause of this dramatic increase in abundance is unknown.<br />

Estimates of abundance <strong>and</strong> trends are available only for the Grays River <strong>and</strong> Lower<br />

Gorge populations. The 10-year trend was negative for the Grays River population <strong>and</strong><br />

just over 1.0 for the Lower Gorge. The Upper Gorge population, <strong>and</strong> all four of the<br />

populations on the Oregon side of the river in the Coastal MPG, are extirpated or nearly<br />

so (McElhaney, Chilcote et al. 2007). However, long- <strong>and</strong> short-term productivity trends<br />

for populations are at or below replacement. Regarding spatial structure, few Columbia<br />

River chum salmon have been observed in tributaries between The Dalles <strong>and</strong> Bonneville<br />

dams. Surveys of the White Salmon River in 2002 found one male <strong>and</strong> one female<br />

carcass <strong>and</strong> the latter had not spawned (Ehlke <strong>and</strong> Keller 2003). Chum salmon were not<br />

observed in any of the upper gorge tributaries, including the White Salmon River, during<br />

the 2003 <strong>and</strong> 2004 spawning ground surveys. Finally, most Columbia River chum<br />

populations have been functionally extirpated or are presently at very low abundance<br />

levels. The loss of off-channel habitat <strong>and</strong> the extirpation of approximately 17 historical<br />

populations increase this species’ vulnerability to environmental variability <strong>and</strong><br />

108

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