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<br />643 of the three categories of spring flows (> I 0,000 cfs, >8,000 cfs, >5,000 cfs). Under the proposed plan, <br />644 the desired frequency and duration of the categories are fully met or exceeded. Because of this, the <br />645 spring flows under the proposed action should meet many of the purposes of the flow <br />646 recommendations, including generation of new cobble sources, creation of channel diversity,provision <br />647 of nutrient loading, maintenance of spawning areas, and creation and maintenance of backwaters and <br />648 other low-velocity habitats. <br /> <br />649 Maintaining low. stable base flows enhances nursery habitat conditions and flows between 500 and <br />650 1,000 cfs optimize backwater conditions-selecting flows at the low end of the range increases the <br />651 availability of water for development and spring releases. Bliesner and Lamarra (2000) reported that <br />652 backwater habitats, which are extremely important for the endangered fish, demonstrated a high degree <br />653 of variability at low flows; but low flows clearly maximized this habitat Juvenile low velocity habitat <br />654 is likely maximized between 800 and 1,000 cfs (Service, 200Id). <br /> <br />655 The proposed plan includes operations to attempt to maintain the base flows in the 500 to 1,000 cfs <br />656 range; however, this cannot always be accomplished. Inflows from tributaries, combined with even <br />657 minimum releases from Navajo Dam, will cause the 1,000 cfs to be exceeded at times. This is <br />658 particularly true during spring runotfwhen downstream tributaries are high and during the frequent <br />659 summer thunderstorms that can add sudden spike flows to the river. In addition, there are difficulties <br />660 with travel time for changed releases to reach critical habitat and discrepancies with gage readings in <br />661 the critical habitat area. <br /> <br />662 Bliesner and Lamarra (2000) report on studies that relate flow levels to habitat creation and <br />663 maintenance and should be referred to for further information. <br /> <br />664 The proposed action will affect water quality in the San Juan River. Releases from Navajo Reservoir <br />665 of high quality water generally dilutes pollutants downstream. This dilution effect will be increased <br />666 during certain periods under the proposed plan but will be decreased in the winter months and <br />667 periodically at other times of the year as releases are reduced. Contaminants of concern include P AHs <br />668 and trace elements such as selenium, arsenic, copper, and zinc. Simpson (1999) concluded "...that the <br />669 concentrations of contaminants in biota inhabiting the main stem of the San Juan River were not <br />670 consistently correlated with instream flow discharges." <br /> <br />671 There is some belief that a more natural hydrograph may result in some natural control of non-native <br />672 fish that compete with the endangered fish. This hypothesis was studied and initial conclusions are <br />673 that a negative response of non-natives to the more natural hydrograph during the test flow period did <br />674 not occur (Brooks, et ai, 2000). <br /> <br />675 Overall, the proposed action should beneficially affect the Colorado pikeminnow and its designated <br />676 critical habitat; water quality changes associated with low flows may have adverse impacts under <br />677 certain conditions when dilution flows are reduced. The proposed action also provides for adaptive <br />678 management so that adjustments can be made to reflect new research and findings. <br /> <br />23 <br /> <br />; , <br />