<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 />
|