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<br />Chapter III Affected Environment and Environmental Consequences 31 <br /> <br />river should increase the primary productivity of the river system during the summer months <br />when temperature controls are in operation. When not in operation, releases would return to <br />pre-existing conditions which are typically very low. <br /> <br />The cycling and amount of nutrients in the tailwaters and lower reaches below Glen Canyon <br />Dam are not well known. While <br />nutrient levels are often at or below <br />detection limits, the fact that there is <br />high biomass of Cladophora <br />glome rata below the dam suggests <br />that nutrients are may not be a <br />limiting factor. The uptake and <br />cycling of nutrients may be quick <br />enough that there is very little <br />opportunity to sample free dissolved <br />nutrients in the water column of the <br />river. Another hypothesis is that <br />delivery rates oflow nutrient levels <br />are sufficient for Cladophora <br />glomerata. Nutrients may also be <br />provided by sediment inputs from <br />below the dam, even in the Lees Ferry <br />reach. Nutrient levels are important <br />to the ecosystem below Glen Canyon <br />Dam. <br /> <br />The existing, post-impoundment, <br />aquatic system is characterized by <br />constant year-round releases of about <br />80C (460F) water that contain low <br />nutrient and low sediment levels. <br />Discharges of clear, cold water from <br />Glen Canyon Dam have permitted the <br />filamentous green alga Cladophora <br />glomerata to capitalize on the few <br />available nutrients released through <br />the dam and other tributary sources. <br />Cladophora and the diatoms depend <br />on these nutrients and form the <br />habitat and food base for an important <br />community of aquatic invertebrates <br />dominated by the amphipod <br />Gammarus lacustris, midges <br />(Chiromomidae), and other aquatic <br />insects. Cladophora, along with the organisms that live on it, forms the basis of a highly <br />productive food chain below Glen Canyon Dam (USDI 1995). <br /> <br />~0.4 <br />0::::: <br />CI <br />E 0.3 <br />~ <br /> <br />gj 0.2 <br />- <br />'1:: <br />G) 0.1 <br />o <br />o <br />01/03 <br /> <br />~0.15 <br />0::::: <br />CI <br />E 0.1 <br />~ <br /> <br />CD <br />lU 0.05 <br />CI <br />-<( <br /> <br />~ <br />i3l 0.04 <br />E <br />~0.03 <br />lU <br />'t:; 0.02 <br />o <br />E 0.01 <br />E <br />-<( <br /> <br />Detritus Releases <br /> <br />_Without Controls <br />o With Controls <br /> <br /> <br />05/03 <br /> <br />08/31 <br /> <br />12/29 <br /> <br />Algae Releases <br /> <br />~Without Controls <br />8 0 With Controls <br /> <br />g E6 <br /> <br />o <br />01/03 <br /> <br /> <br />05/03 <br /> <br />08/31 <br /> <br />12/29 <br /> <br />Ammonia Releases <br /> <br /> <br />_Without Controls <br />o With Controls <br /> <br />o <br />01/03 05/03 08/31 12/29 <br />Figure IO-Extremely low nutrient releases from the <br />dam to the downstream environment would increase <br />with temperature controls. <br /> <br />Since inception of interim flows, the plant component of the aquatic food base has begun to <br />change. The relative dominance of Cladophora in the Glen Canyon reach may already be <br />