Laserfiche WebLink
<br /> <br />20 <br /> <br />6000 <br /> <br />COPEIA, 1996, NO. 1 <br /> <br />DOUGLAS; <br /> <br />5000 <br /> <br />~\ <br />;.: . <br />./ <br />. , ~- <br />. , <br />,I , <br />I I <br />/. I I <br />./ 1/ <br />/ / II <br />, . <br /> <br />. .,.,: <br />'/, \ ' 10 <br />. , , <br />. , , <br />, ., <br />, I <br />. <br /> <br />4000 <br /> <br /> <br />c: <br />.2 <br />;;;3000 <br />~ <br />w <br /> <br />2000 <br /> <br />. <br /> <br /> <br />\}>: <br /> <br />'. <br />~mm~e~0~~~~~~~~~~~~ <br />~ ~ ~ m ~ ~ ~ - ~ ~ ~ ~ ~ ~ ~ m m ~ ~ <br /> <br />1000 <br /> <br />o <br /> <br />MonthlYear <br /> <br />Fig. 4. Bivariate plot of population estimates for <br />1991-1992 by month (solid line) and by month <br />summed over reach (dashed line). <br /> <br />50). The model with the second-highest crite- <br />rion (i.e., the Null model; Mo) is also the simplest <br />in that it presumes that all members of the pop- <br />ulation are equally at risk of capture on every <br />trapping occasion. Burhnam 's estimator (Mb) as- <br />sumes capture probabilities vary with time and <br />with behavioral effects (such as trap-happiness, <br />trap-shyness). The last two models Gackknife <br />estimator Mh, and Chao's Mh) accept that cap- <br />ture probabilities vary by individual animal. <br /> <br />Movement by season within and between reaches.- <br />To determine extent of movement by G. 0Pha <br />within the LCR, capture and subsequent recap- <br />ture(s) for 1992 were compiled by reach and <br />season (Table 3). Because these data reflect <br />numbers of individuals tagged within each reach <br />for a given season then subsequently recap- <br />tured, percentages for each reach and season <br />total 100%. Direct measurements of upstream <br />movement by some tagged fish are provided in <br />Table 3. For G. c)pha tagged at confluence dur- <br />ing winter and subsequently recaptured, 49% <br />(n = 47) were taken upstream in Powell or Salt <br /> <br />reaches during winter/spring. Similarly, of those <br />tagged at confluence during spring and subse- <br />quently recaptured, 51 % (n = 96) were taken <br />upstream during spring/summer. For Powell <br />reach, 18% (n = 7) of recaptures initially tagged <br />there during winter were taken in Salt reach <br />during winter/spring, whereas 31 % (n = 59) of <br />recaptures tagged there in spring were taken at <br />Salt during spring/summer. Overall, 21 % of <br />total movements in 1992 (ascertained by mark/ <br />recapture) was upstream. <br />Elevated population estimates at confluence <br />in Jan./Feb. of 1992 (Fig. 3B), followed by up- <br />stream movement, argue strongly for staging. <br />Estimates at the confluence peaked in early <br />March then gradually decreased through June. <br />A similar peak occurred within Powell Canyon <br />reach in late March, extended into April, then <br />decreased into June. Population size did not <br />peak in Salt Canyon reach until April; estimates <br />remained elevated through June. The last six <br />months of 1992 were similar to that of 1991 <br />(Fig. 3), with estimated population sizes dwin- <br />dling through late summer. However, estimates <br />rose again in autumn 1991 but remained low <br />during a similar period in 1992. <br />Evidence for downstream movement is less <br />convincing (Table 3). OfG. cypha tagged in Pow- <br />ell reach during winter and subsequently re- <br />captured, 21 % (n = 8) were taken at confluence <br />in the remainder of the year. Similarly, 16% (n <br />= 30), and 15% (n = 15) of recaptures tagged <br />at Powell in spring and summer, respectively, <br />were taken at confluence in the remainder of <br />the year. At Salt, 16% (n = 33) and 7% (n = 12) <br />of recaptures tagged in spring and summer, re- <br />spectively, were taken in the two lower reaches <br />over the remaining seasons. Overall, 9% of re- <br />captures in 1992 indicated downstream move- <br />ment. <br />Table 3 primarily reflects population stasis by <br />reach, particularly summer through winter. At <br />confluence, 17% (n = 33) of individuals tagged <br />in spring were subsequently retaken there sum- <br />mer through winter, whereas 76% (n = 54) of <br /> <br />TABLE 3 . ADULT Gila cyp, <br />RIVER DURING A GIVEN SE <br />SEASON (= RCP.SEASON) <br /> <br />TAG REACH TAG SEASO <br />Confluence Winter <br /> <br />Confluence Spring <br /> <br />Confluence Summer <br /> <br />Confluence Autumn <br /> <br />Powell Winter <br /> <br />Powell Spring <br /> <br />Powell Summer <br /> <br />Powell Autumn <br /> <br />Salt Winter <br /> <br />Salt Spring <br /> <br />Salt Summer <br /> <br />Salt Autumn <br /> <br />chub tagged in summel <br />same reach summer th <br />77% (n = 10) of chub <br />autumn were retaken ti <br />Powell, 23% (n = 45) <br />spring were again re( <br />through winter; 78% ( <br />during summer wer, <br />through winter. In ad, <br />those tagged in autumr <br />same reach autumn/wi <br />occurred at Salt, wher <br />dividuals tagged durinf <br /> <br />TABLE 2. POPULATION ESTIMATES GENERATED UNDER FIVE DIFFERENT MODELS (= MODEL) FOR ADULT Gila <br />cyplza WITHIN THE LiTTLE COLORADO RIVER, FROM JULY 1991 THROUGH DECEMBER 1992. Also provided are <br />goodness-of-fit (= CRITERION), with standard deviation of the estimate (= SO), and 95% lower and upper <br />confidence intervals (= LOWER CI; UPPER CI). Models are defined in text. <br /> <br />MODEL CRITERION ESTIMATE SD LOWER CI UPPER CI <br />Pollock and Otto (Mbh) 0.61 4508 120 4330 48 II <br />Null Model (Mo) 0.49 6793 110 6585 7017 <br />Burnham's (M'b) 0.48 8724 920 7242 10,901 <br />Jackknife (Mh) 0.42 10,444 329 9833 11,121 <br />Chao's (Mh) 0.42 8039 210 7648 8472 <br />