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550 <br />MARSH ET AL. <br />TABLE 1.-Summary of numbers of razorback Suckers released as juveniles and later captured during annual March <br />censuses in Lake Mohave, Arizona-Nevada, 1992-2002. The total number of fish captured by release year includes <br />multiple captures of the same fish in different years. <br />Release Number <br />year released 1993 1994 <br />1995 Number captured by capture year <br />1996 1997 1998 1999 <br />2000 <br />2001 <br />2002 Combined <br />1992 131 4 7 2 3 3 1 3 1 2 4 30 <br />1993 1,342 1 3 3 4 3 2 0 2 1 4 23 <br />1994 2,167 0 6 7 4 4 4 5 3 33 <br />1995 1,497 20 13 22 16 11 18 15 115 <br />1996 3,076 5 14 41 26 26 21 133 <br />1997 7,271 2 8 11 12 4 37 <br />1998 7,657 14 16 39 20 89 <br />1999 15,993 2 12 32 22 68 <br />2000 7,159 28 17 45 <br />2001 11,404 1 1 <br />2002 81a 0 <br />Total 57,778b 5 10 5 33 31 45 88 83 163 111 574 <br />a Number released through April 1. <br />b 295 records with duplicate data not included. <br />Five records with unknown release not included. <br />divided into three categories (<_300 mm, 301-350 <br />mm, and >350 mm); the intermediate size-class <br />contains the size release target. Two other factors <br />considered in the analysis were capture status (i.e., <br />captured or not captured in the census year), and <br />census year (i.e., 1999-2002). To eliminate the <br />confounding factor that larger fish were more <br />prone than smaller fish to capture in the first years <br />following release, we imposed an approximate 3- <br />year delay to allow releases to attain a catchable <br />size (e.g., release TL data from repatriates cap- <br />tured in 2002 would include only fish released be- <br />fore January 1, 1999). This delay also allowed fish <br />to experience the majority of size-based posts- <br />tocking mortality and attain lengths at which mor- <br />tality was assumed to be asymptotic with respect <br />to size. <br />We used Program MARK to fit the data to a <br />mark-recapture model and derive maximum like- <br />lihood estimates for apparent survival ((D) and re- <br />capture (p) rates (White and Burnham 1999). This <br />program uses an iterative method to estimate pa- <br />rameters and allows many conceptual models to <br />be fitted and compared. Age-structured (cohort) <br />and time-structured (Cormack-Jolly-Seber) mod- <br />els were initially considered, and size at release <br />was modeled as a covariate of first-year and sec- <br />ond-year survival and recapture rates. Akaike's in- <br />formation criterion (AIC) was used to compare <br />model fit. <br />Growth was examined by fitting the release and <br />capture data from all repatriate captures to a von <br />Bertalanffy Growth (VBG) curve model. Although <br />reparameterized models of the VBG exist specif- <br />ically for mark-recapture studies (e.g., Francis <br />1988; Haddon 2001), the main objective of the <br />VBG for our study was to determine the number <br />of years a fish required to reach adult size after <br />release. This was best achieved utilizing an alter- <br />native method that for a given fish (i.e., per unique <br />PIT tag) used its TL at release and at just one <br />capture or recapture, so that multiple recaptures of <br />the same fish across years did not result in addi- <br />tional growth curve influence. Actual age at re- <br />lease was unknown due to cohort mixing at rearing <br />sites, and thus age-0 denotes age at release into <br />the lake while capture age was the number of years <br />at large after release. A best-fit VBG curve is <br />Li = LJ1 - e-K(,-1o)11 <br />where growth parameters Lco (asymptotic length <br />of the growth curve), K (growth coefficient de- <br />scribing rate at which the asymptotic length is ap- <br />proached), and to (theoretical age at length 0) were <br />assessed using the solver routine in Microsoft Ex- <br />cel 2000 to minimize the sum-of-squared residuals <br />(least squares). Male and female growth rates and <br />maximum adult sizes differ (Minckley 1983; Mc- <br />Carthy and Minckley 1987), and thus, gender-spe- <br />cific curves were generated (juvenile or unknown <br />gender data were omitted). <br />Results <br />The repatriate razorback sucker database con- <br />tained 58,073 releases and 822 capture or recapture <br />records from 1992 through April 2002. After the <br />295 duplicate (same tag number recorded twice) <br />release records were removed, 57,778 release re- <br />cords remained in the database (Table 1). Also, 9 <br />TAI <br />1973) <br />March <br />fish c; <br />repatri <br />triated <br />captu <br />relew <br />recap <br />captu <br />Thus, <br />fish h <br />An <br />estim, <br />from <br />we re: <br />censu <br />The r( <br />captul <br />could <br />lease <br />Am <br />calcul <br />becau <br />timatt <br />captui <br />four e <br />captui <br />(a rec <br />(1973 <br />bias i <br />seven <br />is app <br />erated <br />recapt <br />Fisl <br />350 m <br />numb( <br />of the <br />found <br />ysis: 1 <br />with t <br />size-cl <br />rates i