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

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Life History<br />

Most MCR steelhead smolt at two years <strong>and</strong> spend one to two years in saltwater prior to<br />

re-entering freshwater. Here they may remain up to a year prior to spawning (Howell,<br />

Jones et al. 1985). Within this ESU, the Klickitat River is unusual as it produces both<br />

summer <strong>and</strong> winter steelhead. The summer steelhead are dominated by age two ocean<br />

steelhead. Most other rivers in this region produce about equal numbers of both age one<br />

<strong>and</strong> two ocean steelhead.<br />

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

MCR steelhead were listed as threatened in 1999 (64 FR 14517), <strong>and</strong> their status was<br />

reaffirmed on January 5, 2006 (71 FR 834). The ICBTRT (2003) identified 15<br />

populations in four MPGs (Cascades Eastern Slopes Tributaries, John Day River, the<br />

Walla Walla <strong>and</strong> Umatilla Rivers, <strong>and</strong> the Yakima River) <strong>and</strong> one unaffiliated<br />

independent population (Rock Creek) in this species. There are two extinct populations<br />

in the Cascades Eastern Slope MPG: the White Salmon River <strong>and</strong> Deschutes Crooked<br />

River above the Pelton/Round Butte Dam complex.<br />

Seven hatchery steelhead programs are considered part of the MCR steelhead species.<br />

These programs propagate steelhead in three of 16 populations <strong>and</strong> improve kelt survival<br />

in one population. No artificial programs produce the winter-run life history in the<br />

Klickitat River <strong>and</strong> Fifteenmile Creek populations. All of the MCR steelhead hatchery<br />

programs are designed to produce fish for harvest. However, two hatchery programs are<br />

also implemented to augment the naturally spawning populations in the basins where the<br />

fish are released. The NMFS assessment of the effects of artificial propagation on MCR<br />

steelhead extinction risk concluded that these hatchery programs collectively do not<br />

substantially reduce the extinction risk. Artificial propagation increases total species<br />

abundance, principally in the Umatilla <strong>and</strong> Deschutes Rivers. The kelt reconditioning<br />

efforts in the Yakima River do not augment natural abundance <strong>and</strong> benefit the survival of<br />

the natural populations. The Touchet River Hatchery program has only recently been<br />

established, <strong>and</strong> its contribution to species viability is uncertain. The hatchery programs<br />

affect a small proportion of the species. Collectively, artificial propagation programs<br />

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