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<br />11 <br /> <br />reproductive activities of Colorado squawfish. They further stated that <br />alteration of this hydrological event may affect initiation of Colorado <br />squawfish migration and spawning. Additionally, maintenance of low stable <br />flows in summer and fall are necessary for growth and survival of young <br />Colorado squawfish. <br /> <br />Migration of the Colorado squawfish is cued to the ascending limb and natural <br />spawning is initiated on the descending limb of the annual hydrograph as water <br />temperatures approach 200 C (Tyus and Karp 1989). Spawning, both in the <br />hatchery and in the field, generally occurs in a 2-month timeframe between <br />July 1 and September 1. although high-flow water years may suppress river <br />temperatures and extend spawning in the natural system into September. <br /> <br />Temperature also has an effect on egg development and hatching. In the <br />laboratory, egg mortality was 100 percent in a controlled test at 130 C, At <br />160 to 180 C, development of the egg is slightly retarded, but hatching success <br />and survival of larvae was higher. At 200 to 260 C. development and survival <br />through the larval stage was up to 59 percent (Hamman 1981). Juvenile <br />temperature tests showed that preferred temperatures ranged from 21.90 to <br />27,60 C. The most preferred temperature for juveniles and adults was estimated <br />to be 24.60 C. Temperatures near 240 C also are needed for optimal development <br />and growth of young (Miller et al. 1982). <br /> <br />(:' <br /> <br />':~: <br />.';~ <br /> <br />Ir <br /> <br />;>, <br /> <br />Limited temperature data exist for the San Juan River; however, water <br />temperatures in occupied habitats (as measured at Shiprock and Bluff) currently <br />are well within an acceptable range to expect successful spawning. egg <br />development. and hatching. assuming other habitat/flow conditions are available <br />to the fish. <br /> <br />, <br />i <br /> <br />While consistent temperature data for pre- and post-Navajo Dam conditions do <br />not exist. some important changes can be noted by a review of available data. <br />Olson (1962a), during his preimpoundment study, recorded temperatures as high <br />as 250 C during July and August 1961 near Rosa, New Mexico. on the San Juan <br />River. A short distance downstream near Bl~nco, New Mexico. Olson measured <br />temperatures in excess of 260 C during the same time period. (Tables 1. 2. <br />and 3. Appendix C) <br /> <br />Recent temperature readings document a significant change since the closure of <br />the Navajo Dam. In July 1989, the New Mexico Department of Game and Fish <br />measured 130 C on the San Juan River at the Highway 64 bridge crossing, just <br />upstream of Blanco. New Mexico. Cold-water releases from the Navajo Dam and <br />their effect on water temperature in the San Juan River can be seen as far <br />downstream as Farmington, New Mexico. and the confluence with the Animas River. <br />Downstream of Farmington, ambient air temperature and. to a lesser extent. the <br />warmer water from the Animas River tend to ameliorate the effect of cold-water <br />releases from the Navajo Dam throughout currently occupied Colorado squawfish <br />habitat. Post-Navajo water temperatures on the San Juan River at Farmington, <br />New Mexico, and particularly at Bluff, Utah, are still warmer for a longer <br />period of time than anywhere else in the Upper Basin. (Tables 4 and 5, <br />Appendix C) <br /> <br />" <br /> <br />". <br />~';:,'; <br /> <br />, <br />k ~. <br /> <br />~<.~ <br /> <br />'", <br /> <br />.c;, <br /> <br />