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Study Timetable and Direction <br />This evaluation was originally developed and scheduled for three years. <br />The first two years (FY98 and FY99) were planned for field collections and FY2000 <br />for preparing the final report. Study direction was changed in August 1998 when <br />the RIP Management Committee discontinued all field work previously scheduled for <br />the spring, summer, and fall of 1999 (March through September). The only field <br />work scheduled for FY99 was conducted during October 1998. Analyses of the field <br />data and preparation of the final report were accomplished in FY99 instead of <br />FY2000. To accomplish the necessary objectives for a 2-year field evaluation, <br />the field methodology and study design were initially developed for 2 years of <br />field work, not 1 year. Consequently, less information was collected because one <br />year of field work was canceled, and therefore, study objectives were not <br />sufficiently addressed and some of the end products were not met. <br />STUDY AREA <br />This evaluation included the Upper Colorado River from RM 187.6 immediately <br />downstream from the Price-Stubb Dam (RM 188.3) to Loma (RM 152.6) and the Lower <br />Gunnison River--RM 3.0-0.7. Fish collections with electrofishing were conducted <br />exclusively in a 4.6-mile section of the Colorado River from RM 187.6 to RM <br />183.0. Telemetry from boats was conducted from Colorado River RM 185.5 to RM <br />152.6 and the lower 2.3 miles of the Gunnison River (Figure 2). <br />METHODOLOGY <br />Field efforts for this evaluation relied on two separate techniques, mark <br />and recapture and telemetry, both applied independently to determine if sub-adult <br />and adult fish would use the passageway to pass over the GVIC Diversion Dam. The <br />first method involved collecting native and nonnative fish with electrofishing <br />and marking them from the first 2 miles of river immediately downstream of the <br />diversion dam. Although the passage structure was constructed to provide passage <br />primarily for Colorado pikeminnow, surrogate native and nonnative fishes were <br />also marked and tagged because Colorado pikeminnow numbers inhabiting the study <br />area were low and determining if and when pikeminnow would use the fish passage <br />at this site might take considerable time. <br />Sub-adult and adult fish of the most common large-sized, native fishes <br />(flannelmouth sucker, bluehead sucker, and roundtail chub) were initially <br />inserted with a Passive Integrated Transponder (PIT) tag and released. An <br />administrative decision was made in mid-August 1998 to discontinue field work for <br />the following year. Use of PIT tags was discontinued and it was decided that a <br />short-term mark (i.e., fin clip) would suffice for the remainder of the study. <br />Therefore, between 3 April and 27 April and between 17 July and 20 August 1998, <br />all native fishes captured were PIT tagged. Between 24 and 28 August 1998, all <br />native fishes were fin clipped. Other common sub-adult and adult nonnative <br />fishes such as common carp and white sucker that were captured were marked with <br />an external, individual, serially-numbered Floy~ "spaghetti" tag in the dorsal <br />musculature. Rainbow trout, brown trout, and sucker hybrids (white sucker X <br />flannelmouth sucker, white sucker X bluehead sucker. and bluehead sucker X <br />4 <br />