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<br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br /> <br />summary of the category 1 and 2 curves identified at Workshop #1 is presented <br />in Table 5. <br /> <br />Generally, the same line of reasoning was used at each cd terion or <br />decision point for all three species. The following presents a summary of the <br />manner in which the experts dealt with each of the nine criteria: <br /> <br />1. Life stage. Data for all three species were partitioned by life stage <br />because the experts felt that the fish exhibit different habitat use by size or <br />age. It was pointed out that this use does not necessarily change with <br />physiological life stage (larval, YOY, juvenile, adult), but may best be <br />described by size categories. Thus, the life stages proposed by FWS were <br />retained for the razorback sucker, but were modified for the humpback chub and <br />Colorado squawfish (Table 4). <br /> <br />The experts agreed that riverine conditions need to be identified to allow <br />for spawning migration and passage/access by Colorado squawfish and razorback <br />sucker. However, they felt that using depth, velocity, and substrate <br />measurements from the current database could not adequately describe these <br />needs. Although an adult migrating to a spawning area may swim over a great <br />variety of habitats, its success may be determined entirely by sufficient water <br />depth and adequate velocity. Temperature was identified as an important key to <br />the onset and act of migration, but it was noted that the database does not <br />contain adequate data to develop a temperature curve. <br /> <br />Passage/access was distinguished from migration in that the former is more <br />site specific and involves all life stages moving both up- and downstream. The <br />experts felt that site-specific criteria need to be developed for passage <br />through artifical structures, such as dams and water diversions, as well as <br />dewatered regions of river. It was also pointed out that access to highwater <br />backwaters and other riverside habitats is essential, but also site specific. <br />The experts felt that fish passage is an important consideration which should <br />be identified as a data gap. <br /> <br />2. River. The experts agreed that for all life stages of each species the <br />data should be partitioned by river, i.e., Colorado, Green, Yampa, etc., except <br />where there were no perceived differences in habitat use among these rivers, or <br />where there appeared to be insufficient data to treat each separately. In many <br />cases, the experts felt that there may not be differences in habitat use among <br />rivers, but they wanted to partition the data and run statistical tests. If no <br />significant differences were revealed, data from different rivers were pooled <br />by the experts in Workshop #2. Also, data from tributaries were pooled with <br />data from main rivers where the data came from the tributary mouths; i.e., data <br />on nonspawning adult razorback suckers from Ashley Creek, pariette Wash, and <br />the Duchesne River were pooled with data from the Green River because these <br />tributary mouths were considered habitats of the Green River. For size 5 <br />Colorado squawfish, data from Ashley Creek, pariette Wash, and Brush Creek were <br />pooled with the Green River, but data from the Duchesne were separated because <br />the observations were above the mouth of this tributary. <br /> <br />13 <br />