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<br />The Forest Service (FS) and state wildlife agency later contributed to this impact and furthered the <br />BCT decline by significant increases in fish stocking activities on national forest streams and lakes, <br />including waters off NFS lands. In 1930, some 34.6 million fish were planted on NFS waters alone. <br />The NB cutthroat became extirpated in the Utah Lake system in the early 1930's, a victim of wide- <br />spread harvest, exotic introductions, and habitat-flow loss through irrigation diversions (Cope 1955, <br />USDA FS 1984, Hickman 1978). <br /> <br />The historical NB riverine habitat was estimated by this assessment at 1,178 stream miles within the <br />four major sub-basins (Table 6c). About 38% of these stream miles were historic habitat on three <br />national forests (Wasatch-Cache, Uinta, and Manti-LaSaI NF's). Occupied habitat occurs only on one <br />NF totaling 7.5 stream miles for four known NB populations, of which two are remnants and two are <br />transplants from remnant stocks (Table 4,5). These existing populations occupy only 1.6% of historic <br />national forest habitat. Human activities have caused extirpation of NB populations over an estimated <br />99% of historic sub-basin waters, and 98% on national forests waters. One NB remnant population <br />recently discovered occurs off national forest lands in the Parley's-Lambs Creek watershed, Jordan <br />River sub-basin (Woolf 1995). Expansion of this population onto the Wasatch-Cache NF in this <br />watershed is probable in the future through State management actions. The status of two NB <br />transplanted populations was recorded as .secure, expanding. (SEX). These populations in the <br />Wasatch-Cache NF, occur in a reservoir and stream within the Red Butte Natural Research Area, a <br />protected NF watershed. However, the reservoir could be eliminated in the future due to structural <br />instability, therefore, severely reducing the BCT population and its use as a brood stock area. Habitat <br />condition is indicated as "good. and trend in abundance is .increasing. (Table 13). Status of the two <br />remnant populations, one each in the Weber River and Jordan River sub-basins is .at-risk, declining" <br />(ARD) in the Weber River and .secure, expanding. (SEX) in the Jordan River. National forest activities <br />and man's encroachment continue to place these populations .at-risk.. While habitat trend is .stable" <br />for both populations, overall condition varied from "fair" for the Weber River to .good" for the Jordan <br />River populations. <br /> <br />All four populations have had genetic evaluation completed (100%) for meristics and electrophoretic <br />validation as pure populations, and 75% have been validated with mONA (Table 7). Exotic fish, <br />primarily rainbow trout and other cutthroat trout are present in or immediately adjacent to 100% of <br />the occupied habitats, and are viewed as a threat to all populations. All populations are considered <br />resident in streams, and all are rare in abundance. Habitat condition factors have not impacted two <br />of the three Jordan River sub-basin populations. But one population, in and adjacent to the Twin <br />Peaks Wilderness, Is subject to angling pressure and declining population. The Weber River popula- <br />tion is affected by dewatering, lack of woody debris, changes in channel morphology, and streambed <br />sedimentation, primarily associated with livestock grazing activities (Table 15). <br /> <br />There is still considerable uncertainty regarding possible suspect NB populations. Two populations <br />(Ogden and Spanish Fork sub-basins) are suspect but need further genetic evaluation to ascertain <br />pure status. Initial genetic testing is cautious in assuming purity because of possible intermixing and <br />close association with Yellowstone cutthroat trout and BRB populations (Dennis Shiozawa, Brigham <br />Young University, personal communications 1996). But efforts are underway by the Wasatch-Cache <br />NF and Utah Division of Wildlife Resources to investigate certain additional waters as part of the BCT <br />conservation strategy for Utah (UDWR 1996). <br /> <br />Southern Bonneville <br /> <br />The assessment area includes that portion of the Bonneville Basin within the Sevier River and <br />Escalante Lake sub-basins in south-central Utah. Included within this historic habitat range are nine <br /> <br />50 <br />