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<br /> <br /> HUMPBACK CHUB ADU (260+mm) <br /> , (1,9.0.40.1.1.0.20.0) 20 <br /> a.. n . 286 <br /> 16 <br />z ~ <br />0 a.. <br />~ z <br /> w <br />... 10 ;:) <br />::::i 0 <br /> w <br />j: 0.4 rr <br />;:) ... <br /> 6 <br /> 0.2 <br /> 0 <br /> 10 20 30 40 <br /> DEPTH (leet) <br /> , (1,0.27,3.9,1.0,60.0) 40 <br /> a.. n . 274 <br />Z 30 <br />0 0.8 ~ <br />~ z <br />... w <br />::::i 20 ;:) <br />j: 0.4 0 <br />;:) w <br /> rr <br /> ... <br /> 0.2 10 <br /> 0 0 <br /> 0.0 1.0 2.0 3.0 4.0 <br /> VELOCITY (lpa) <br /> o.a <br />z <br />0 o.a <br />~ <br />... <br />::::i 0.4 <br />j: <br />;:) <br /> 0.2 <br /> 0 <br /> <br /> <br /> <br /> <br />CL SI SA GR RU BO BE OT <br />SUBSTRATE <br /> <br />FIGURE 6. Raw data and interim suitability in- <br />dex curves for depth, velocity, and substrate for adult <br />humpback chub (n = number of observations or in- <br />dividual fish). <br /> <br />by the adults was similar although discon- <br />tinuous. They also decided to pool the data <br />for all gears, although there was concern <br /> <br />that electrofishing data may reflect a fish <br />forced to move from preferred microhab- <br />itat to the capture site. Of equal concern <br />was the belief that passive gears such as <br />trammel and gill nets may intercept fish <br />moving between desired microhabitats. <br />Although radiotelemetry data were pre- <br />ferred, there were insufficient numbers of <br />observations for 51 curve development, and <br />the conventional gear data were also used. <br />Because the microhabitat data were se- <br />cured from different gear types, the curve <br />set received a confidence rating of B. The <br />average depth used by adults was 10.3 feet <br />with a maximum of 40.1 feet, and average <br />velocity was 0.6 fps with a range of 0 to <br />3.9 fps (Table 1; Figure 6). The depth curve <br />was dramatically modified by the experts <br />to reflect adult use of all water depths <br />greater than about 7.2 feet. The experts felt <br />that the smaller sample size from greater <br />depths reflected gear inefficiency and not <br />reduced use by the fish. Although the <br />species is known to inhabit regions with <br />depths of 40 feet or greater, the experts felt <br />that electrofishing was consistently effec- <br />tive to only about 10 feet depth, while gill <br />and trammel nets were difficult to set ef- <br />fectively at the greater depths, and radio- <br />telemetry transmission was reliable from <br />only about 12 feet of depth. Most of the <br />data from the greater water depths resulted <br />from netting and angling captures. The <br />adults were found over boulders and bed- <br />rock with intervening deposits of silt and <br />sand. The curve set for adults was applied <br />to the Upper Colorado River Basin from <br />March to November and was not restricted <br />by the general habitat constraint. No <br />spawning curve was developed for this <br />species because the experts felt that not <br />enough was known about its spawning ac- <br />tivities. <br /> <br />DISCUSSION <br /> <br />The 51 curves developed from this proj- <br />ect were based on the best field data and <br />information available for the humpback <br />chub in the Upper Colorado River Basin. <br />These curves were developed by species <br />experts through consensus and peer re- <br />view, and reflect the microhabitat data col- <br />lected in the upper basin from 1964 through <br />1986. Readers should be cautioned that the <br />species experts classified these as "interim <br /> <br />I~ 40 <br /> <br />51 curves" and presently recommend ap- <br />plication of the adult curve set, recogniz- <br />ing that much information still needs to <br />be gathered on the rare fishes of the upper <br />basin. The experts recommended refining <br />these curves as more data become avail- <br />able. <br />The process by which these 51 curves <br />were developed is recommended in deal- <br />ing with large volumes of pre-existing mi- <br /> <br />Rivers · Volume 1, Number 1 <br /> <br />J an uary 1990 <br /> <br />crohabitat informat <br />many literatu~e ~Ot <br />concept of asslmlla <br />uation by a panel I <br />sound in that it aIle <br />by the experts with~ <br />amounts of time to 1 <br />the data. The idea I <br />which experts and I <br />equal opportunity tl <br />worked well. HOWl <br />participants felt tl <br />should have been h, <br />use of the 51 curves i <br />and generation of <br />This would have ~ <br />voice their judgml <br />soundness of the st <br />lationships. <br /> <br />Armour, C. L., R. <br />cedures (HE! <br />sources. Was} <br />Bovee, K. D. 198: <br />methodology <br />Wildlife Serv <br />-. 1986. Dl <br />stream flow i: <br />ington, DC: l <br />Bovee, K. D., ani <br />probability-o <br />Fish and WH <br />Crance, J. H. 191 <br />Inland stocks <br />82110.85). <br />-. 1987. H <br />nique. North <br />Glova, G. J. 1982 <br />16-27 in R. .I- <br />Zealand Min <br />47). <br />Haan, C. T. 1977 <br />Holden, P. B. 19 <br />Green River, <br />Larimore, R. W., <br />fishes. F isheri <br />Linstone, A. A., , <br />Wesley. <br />Milhous, R. T. 1 <br />Levine, editc <br />Society for C <br />Milhous, R. T., [ <br />simulation sJ <br />Orth, D. J., and ( <br />ommending <br />413-445. <br /> <br />I R. A. Valdez et c <br />