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Yampa River discharge peaked. During summer, release levels were designed to maximize <br />nursery habitat for Colorado pikeminnow near and downstream of Jensen, Utah (Tyus and Karp <br />1991). To achieve the desired stable base flow of 51 m3/sec ( ± 12.5%, Pucherelli et al. 1990, <br />Tyus and Karp 1991, U. S. Fish and Wildlife Service 1992), releases were usually decreased to <br />as low as 22.3 m3/sec soon after prescribed high spring flows ended because Yampa River <br />discharge was usually high. Dam releases were increased later in summer after Yampa River <br />discharge declined and when Green River discharge at Jensen fell below target levels. <br />Water temperatures in the Green River upstream of the Yampa River in the period 1992 <br />to 1996 showed a slightly warmer summer pattern than for the previous 1978 to 1991 period as <br />summer maxima typically peaked at about 18°C or less for a short period (Bestgen and Crist <br />2000). Summer discharge manipulations altered thermal regimes in the regulated reach because <br />flow level and water temperature were inversely correlated in the Green River downstream of <br />Flaming Gorge Dam (Vanicek et al. 1970, Bestgen and Crist 2000). This is because reservoir <br />releases that are cold relative to air temperature progressively warm via solar insolation <br />downstream from the dam, but warm faster in upstream reaches if flows are lower and slower. <br />Thus, under low drought flows, relatively warm water can be expected well upstream into <br />Browns Park if air temperatures are warm. Dynamics of flow and water temperatures and <br />regression models to predict downstream warming were discussed in detail in Bestgen and Crist <br />(2000) and Muth et al (2000). Because flows typically increased from Flaming Gorge Dam later <br />in summer during 1992 to 1996, maximum temperatures were sometimes achieved in late June <br />but often declined by mid July. <br />Flow and temperature regimes in the Green River downstream of Flaming Gorge Dam <br />since 1997 followed elements of both the 1992 Biological Opinion and newer proposed <br />recommendations. Higher spring releases were realized in 1997 and 1999 (Fig. 5), but spring <br />peaks during study years 2002 to 2004 were at or below power plant capacity (about 130 m3/sec, <br />Fig. 4). Compared to earlier post-regulation periods, in 1997 to 2004, and particularly for 2002 <br />to 2004 study period (and in 2000 and 2001), base flows (August to February) were lower, <br />stable, and more closely approximated the historical hydrograph (Fig. 6, Table 1). Flows that <br />16