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<br />o <br />o <br />C. <br />tu <br />C.;l <br />o <br /> <br />5 <br /> <br />Mr. Calvin Joyner <br /> <br />land or water ownership or management. The Service has identified water, <br />physical habitat, and biological environment as the primary constituent <br />elements. This includes a quantity of water of sufficient quality that is <br />delivered to a specific location in accordance with a hydrologic regime that <br />is required for the particular life stage for each species. Water depletions <br />reduce the ability of the river system to provide the required water quantity <br />and hydrologic regime necessary for recovery of the fishes. The physical <br />habitat includes areas of the San Juan River system below Farmington, New <br />Mexico, that are inhabited or potentially habitable for use in spawning and <br />feeding, as a nursery, or serve as corridors between these areas. In <br />addition, oxbows, backwaters, and other areas in the 100-year floodplain, when <br />inundated, provide access to spawning, feeding, and nursery habitats. Water <br />depletions reduce the ability of the river to create and maintain these <br />important habitats. Food supply, predation, and competition are important <br />elements of the biological environment. Food supply is a function of nutrient <br />supply and productivity, which could be limited by reduction of high spring <br />flows brought about by water depletions, Predation and competition from <br />nonnative fish species has been identified as a factor in the decline of the <br />endangered fishes. Water depletions contribute to alterations in flow regimes <br />that favor nonnative fishes. The Service concludes that the pre-1983 water <br />depletions impact the primary constituent elements and cause destruction or <br />adverse modification to critical habitat. The Service concludes the post-1982 <br />and proposed depletions do not cause destruction or adverse modification to <br />critical habitat provided that they do not exceed the 3,000 acre-foot <br />cumulative depletion. <br /> <br />8IOLOGICAL BACKGROUND <br /> <br />A marked decline in Colorado squawfish and razorback sucker populations can be <br />closely correlated with the construction of dams and reservoirs between the <br />1930's and the 1960's, introduction of nonnative fishes, and removal of water <br />from the Colorado River system. Behnke and Benson (1983) summarized the <br />decline of the natural ecosystem. They pointed out that dams, impoundments, <br />and water use practices are probably the major reasons for drastically <br />modified natural river flows and channel characteristics in the Colorado River <br />Basin. Dams on the main stem Colorado and San Juan Rivers have essentially <br />segmented the river systems, blocking Colorado squawfish and razorback sucker <br />spawning migrations and drastically changing river characteristics, especially <br />flows and temperatures. In addition, major changes in species composition <br />have occurred due to the introduction of nonnative fishes, many of which have <br />thrived as a result of changes in the natural riverine system (i.e., flow and <br />temperature regimes). The decline of endemic Colorado River fishes seems to <br />be at least partially related to competition or other behavioral interactions <br />with nonnative species, which have perhaps been exacerbated by alterations in <br />the natural fluvial environment. <br /> <br />As the southernmost tributary of the Upper Colorado River Basin, the San Juan <br />River peaks earlier in the year and attains warmer water temperatures than <br />other Upper Basin streams and is conducive to longer and better growth <br />potential for young Colorado squawfish and razorback suckers, Any additional <br />large loss of water or further degradation of remaining habitats of the San <br />Juan River will exacerbate problems the Colorado squawfish and razorback <br />