Laserfiche WebLink
<br />. <br /> <br />. <br /> <br />Wintering bald eagles were first observed to congregate in Grand Canyon in the early <br />1980's and the winter population there increased dramatically after 1985 (Brown et aI., <br />1989, Brown and Stevens 1991, Brown and Stevens 1992). The wintering bald eagle <br />population has been monitored since 1988, and it occurs throughout the upper half of <br />the Grand Canyon (in Marble Canyon) and on both Lakes Powell and Mead. Density of <br />the Grand Canyon bald eagles during the winter peak (in late February and early <br />March) ranged from 13 to 24 birds between Glen Canyon Dam and the LCR confluence <br />from 1993 to 1995 (Sogge et aI., 1995). <br /> <br />A concentration of wintering bald eagles occurs in late February at the mouth of <br />Nankoweap Creek, where bald eagles forage on spawning rainbow trout (Brown et aI., <br />1989, Brown 1993). Bald eagle density there ranged from 6 in 1987 to 26 in 1990, and <br />18 bald eagles occurred at Nankoweap Creek in 1995 (Sogge et aI., 1995). Eagle <br />density was correlated with trout density in the lower 0.5 km of Nankoweap Creek, and <br />trout density was correlated with tributary stream water temperature (Leibfried and <br />Montgomery 1993). Territorial behavior, but no breeding activity, has been detected in <br />Grand Canyon. <br /> <br />Life Requisites <br /> <br />At Nankoweap Creek in Grand Canyon, wintering bald eagles preferentially capture <br />rainbow trout in the shallow creek, rather than in the mainstream where foraging <br />success is low (Brown 1993, Sogge et aI., 1995). Bald eagles at Nankoweap Creek <br />prefer roosting and feeding areas that are relatively free of vegetation. The eagle <br />population there consists of all age classes, with considerable piracy and other <br />interactions between individuals (Brown and Leibfried 1990, Brown and Stevens 1991). <br />The ease and relative safety of foraging in Nankoweap Creek affords wintering bald <br />eagles at Nankoweap Creek the opportunity to accumulate energy reserves needed for <br />their long, northward migration flights and initiation of nesting. <br /> <br />Bald eagle distribution in Glen and Grand canyons appears to be negatively related to <br />human disturbance (Brown and Stevens 1997). Although bald eagles are widely known <br />as opportunistic foragers, they are rare in the Glen Canyon and uppermost Grand <br />Canyon reaches. This is surprising given that those reaches contain the most abundant <br />aquatic food base and trout populations (Stevens et al. 1997c). Those reaches support <br />the highest intensity of recreation and other human uses, and Brown and Stevens <br />(1991) reported that bald eagles in Grand Canyon are extremely sensitive to human <br />disturbance, often abandoning their foraging sites when human came within 0.5 km. <br />For these reasons, Brown and Stevens (1997) concluded that human disturbance is <br />responsible for the general rarity of bald eagles in the upper reaches. <br />Impacts of BHBFs and Conclusions <br /> <br />Wintering and migrant bald eagles have largely left the Grand Canyon region by late <br />March (Stevens et al. 1997b). The few remaining eagles in April forage <br />opportunistically and may continue to catch trout in the mainstream. The rainbow trout <br /> <br />1998 GCD Beach/Habitat Building Flow 17 <br /> <br />Biological Assessment <br />