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<br />238 <br /> <br />~~tj 10 <br />~b\v <br />I~ l' \A1'10 <br />~?~I~O vrJ <br /> <br />COGGINS ET AL. <br /> <br />10,000 I <br />.~ 8,000 <br />j 6,000 <br />~ 4,000 <br />o <br />"- 2,000 <br />o I I I I I I I I I I I <br />,# ,,f,'I' ~'" ,,f,'I'" ,,f,'I'" i' ,0,0,'0 ,0,0," ,,f,'I"o ,$' 0,,# o,,~' o,,~'" o,,~'" <br /> <br />I I I <br /> <br />Year ~ <br /> <br /> <br />~(}~~ev -t ~l~ .o(\.t ~ <br />'1110 \_~~ <br />7 v \~V <br />~ <br /> <br />7.000 <br />~ 6,000 <br />Vi 5,000 <br />_2 4.000 <br />~ 3.000 <br />g- 2.000 <br />"- <br />1.000 <br />o <br /> <br />,o,rf' ,0,,,,, ~",o" ~",,,, ~q> ,0,,,,,> ,<It ,,f,'I" ~","o ,$' 0,,# 'f'<>' ",~o" 'f''i;)'" <br /> <br />Year <br /> <br />FIGURE 3.-Abundance estimates for humpback chub from <br />closed-population capture-recapture models in the Little <br />Colorado River (top panel; all estimates for fish larger than <br />ISO mm total length) and the Little Colorado River inflow <br />reach of the Colorado River (bottom panel; all estimates for <br />fish larger than 200 nun total length). In the top panel, the <br />estimates depicted as diamonds are from the studies of <br />Douglas and Marsh (1996) and those depicted as squares are <br />from this article. In the bottom panel, the estimates depicted as <br />diamonds are from the studies of Valdez and Ryel (1995) and <br />that depicted as a square are from the studies of Trammell and <br />Valdez (2003). The error bars in both panels indicate 95% <br />confidence intervals. <br /> <br />sampling coverage throughout the entire reach. Annual <br />sample sizes in 1994-2000 and 2002--2003 were <br />between 2% and 50% of the 1990--1993 average <br />sample size, and in some years effort was focused near <br />the LCR confluence. The lack of robust coverage and <br />limited sampling in the mid to late 1990s suggest that <br />comparing the 1990-1993 and 2001 data best depicts <br />the overall trend of relative abundance. However, <br />though both data sets suggest an overall decline in <br />adult humpback chub abundance, simple linear re- <br />gression analyses provide estimated slopes that are not <br />significantly different from zero (P = 0.14 for both <br />regressions; Figure 2). <br /> <br />Closed-Population Models <br /> <br />Population size estimates for fIsh (TL > 150 mm) <br />from the Chapman-modified, Lincoln-Petersen closed- <br />population model ranged from about 2,000 in 2001 to <br />about 3,400 in 2003, a decline from the 4,300-5,400 <br />individuals estimated in the 1990s (Figure 3). Recent <br />closed-population abundance estimates in both the <br />LCR and the LCR inflow reach (Figure 3) suggest <br />smaller population sizes in the early 2000s than in the <br /> <br />early 1990s, although the preclSlon for all Lin- <br />coln-Petersen estimates is low. <br /> <br />Open-Population Models <br /> <br />The bootstrap goodness-of-fIt test in MARK was <br />able to calculate a C to adjust for the overdispersion of <br />the data. This estimate was used to evaluate the effects <br />of overdispersion on AlCc model selection. No changes <br />in model selection were found across the range of c <br />values evaluated. The best (lowest AlC) Jolly-Seber <br />model for estimating mortality and capture probability <br />was the age-dependent mortality and time-dependent <br />capture probability model (Table 2). Annual mortality <br />decreased with age, from about 68% for age-2 fIsh to <br />about 16% for fIsh over age 15 (Figure 4). Mortality <br />estimates from each of the ASMR model formulations <br />were similar to those of the Jolly-age methods; these <br />estimates were age dependent and ranged from about <br />65% for age-2 fIsh to about 18% for fIsh over age 15 <br />(Figure 4). <br />Annual capture probabilities were consistent across <br />all models. Annual capture probability for the Jolly- <br />age model ranged from 0.04 to 0.51 (Figure 4). Capture <br />probability from the three ASMR model formulations <br />was similar, ranging from about 0.04 to 0.47 (Figure <br />4). In both the ASMR and Jolly-age models capture <br />probability was highest in the early 1990s, when <br /> <br />0.8 <br />~O.7 <br />~0.6 <br />'; 0.5 <br />50.4 <br />~0.3 <br />$ <br />C 0.2 <br />..:10.1 <br />o <br /> <br />- ASMRI <br />---.- ASMR2 <br />...... ASMR3 <br />_.~. Jolly-Ab'" <br /> <br /> <br />4 <br /> <br />6 <br /> <br />10 II 12 13 14 15 <br /> <br />8 9 <br />Age <br /> <br />0.6 <br />&'0.5 <br />:0 <br />.8 0.4 <br />o <br />.t 0.3 <br />~o.2 <br />Q. <br /><30.1 <br />0.0 <br /> <br />,0,"0'" ,o,rf' ~o,' ,,f,'Io,, ,0,0,'> ,,f,'I'" ,,,,,,,'> ,<>,0,'0 ~o," ,,,,0,"0 ,,,,,f,'I o,,~<> o,,~' <br /> <br />- ASMR I <br />---ASMR2 <br />ASMR 3 <br />--~ Jolly-Age <br /> <br /> <br />Year <br /> <br />FIGURE 4.-Humpback chub annual mortality rates across <br />ages (top panel) and capture probabilities across years (bottom <br />panel) from the three formulations of the annual age- <br />structured, open-population capture-recapture (ASMR) model <br />and the age-structured Jolly-Seber model. The error bars on <br />the ASMR estimates are 95% credible intelVals from Markov <br />chain-Monte Carlo sampling of posterior parameter distribu- <br />tions; those on the Jolly--Seber estimates are 95 % confidence <br />intelVals. <br />