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7/14/2009 5:01:45 PM
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UCREFRP
UCREFRP Catalog Number
7399
Author
Valdez, R. A., P. B. Holden and T. B. Hardy
Title
Habitat Suitability Index Curves for Humpback Chub of the Upper Colorado River Basin
USFW Year
1990
USFW - Doc Type
Rivers
Copyright Material
YES
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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 />
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