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<br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br /> <br />0U2J86 <br /> <br />cover and soil stabilization currently provided by such species. The same can be said for <br />the south campground site located at the Williams Fork River inlet to the Williams Fork <br />Reservoir, which, although it supports no noxious weeds, is populated by a diverse <br />community of common weeds, <br /> <br />Williams Fork Project shorelines are open to dispersed recreation and are subject to <br />heavy use. Evidence of dispersed recreation use is especially noticeable south of the west <br />campgroundlboat launch area, The weed problem at the Williams Fork Project will likely <br />increase if use of these current dispersed recreation sites increases in the future or if <br />dispersed recreation comes to involve more of the project shoreline. A recreation <br />management plan component that would discourage overuse of current dispersed <br />recreation sites and would moderate or limit further encroachment on undisturbed sites <br />will protect and enhance Williams Fork Project habitats by preventing impacts to native <br />soils and vegetation. Likewise, a plan to prevent overuse of the existing recreation <br />facilities will assist in preventing possible expansion of existing noxious and common <br />weed populations there and in preventing invasion of these sites by additional noxious <br />and common weed species. <br /> <br />4.2 Meadows <br /> <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br /> <br />As discussed above, the largest colonies of Canada thistle encountered at the Williams <br />Fork Project do not seem to be the result of site disturbance but rather that the species has <br />invaded healthy native range, pasture, or meadow communities in response to a favorable <br />moisture regime, These sites are not heavily used by recreationists or even probably <br />observed very often by the public, and so the presence of Canada thistle does not pose a <br />resource risk in that sense or, consequently, warrant its control at these sites. <br /> <br />The potential for spread of Canada thistle by seed from these sites to other similar sites or <br />to sites that are currently disturbed or that may be disturbed in the future is an attendant <br />resource risk. However, given the enonnously wide distribution of this cosmopolitan <br />weed and the doubtless huge seed reservoir in local and regional soils, the additional <br />contribution of seed from these few sites is probably not significant. If this type of <br />infestation is, in fact, simply an opportunistic colonization of sites with moisture regimes <br />favorable to Canada thistle, attempts to exclude it from such sites may be futile through <br />time, <br /> <br />4.3 Spoil Piles <br /> <br />During the Scoping Meetings, the potential for noxious weed growth on existing spoil <br />piles at the Williams Fork Project and the need for control measures were mentioned as <br />potential issues, The spoil piles in question were surveyed during the noxious weed <br />survey, and no noxious weeds were encountered, However, a wide variety of common <br />weeds, including pennycress, lambsquarters (Chenopodium album), tumblemustard, <br />Russian thistle (Salsola sp,), mullein, kochia (Kochia scoparium), pigweed (Amaranlhus <br />sp.), creeping knotweed (Polygonum aviculare), foxtail, and others, has colonized these <br /> <br />Williams Fork Reservoir <br />Hydroelectric Project <br />January 2004 <br /> <br />Steiger:; CorpomllOn <br />No:<ious Weed Survey Report <br /> <br />Page 10 <br />