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<br />Renrod,~ action <br />Razorback suckers have been captured in breeding condition in many different habitats <br />and environmental conditions. Spawning has been documented in mainstream rivers, ' <br />riverine-influenced areas of large impoundments, and wave-washed shorelines of <br />reservoirs. The ability to use a variety of habitats and flow conditions ma reflect <br />Y <br />adaptations to conditions in the historic Colorado River system. However, the absence <br />of any substantial level of recruitment makes it difficult to determine the habitat and flow <br />conditions that would be the most suitable for recovery efforts.. It is not known whether <br />all life history requirements can be met in either the mainstream river or an ' <br />impoundment. For clarity, the following discussion of reproductive requirements and , <br />habitat use is separated into lacustrine and riverine habitats. <br />Lacustrine habitats. The largest surviving stock of razorback suckers exists in <br />Lake Mohave in the lower Colorado River basin. Successful spawning has been <br />documented in Lake Mohave and numerous larvae have been collected Bozek et al. <br />( <br />1990, Marsh and Langhorst 1988). However, juveniles have been extremely rare in ' <br />collections (Minckley et al. 1991). Spawning in Lake Mohave and other lower basin <br />reservoirs occurs eariy in the year, from January through April/May (Medal-Ulmer 1983, <br />Langhorst and Marsh 1986, Mueller 1989). Water temperatures during spawning ' <br />ranged from 11.5-18°C (52.7-64.4°F) (Douglas 1952, Model-Ulmer 1983, Langhorst ' <br />and Marsh 1.986). Spawning fish congregate and spawn in flat or gently sloping <br />shoreline areas over gravel, cobble, or mixed substrate types (Douglas 1952, Medal- ' <br />12 , <br />~J <br />