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Last modified
7/14/2009 5:01:47 PM
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5/20/2009 11:06:44 AM
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UCREFRP
UCREFRP Catalog Number
9334
Author
Stickney, R. R.
Title
Editor
USFW Year
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USFW - Doc Type
1993
Copyright Material
YES
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WILLIS, MURPHY, AND GUY REVIEWS IN FISHERIES SCIENCE <br />PSD would be higher because females would be more abundant at that time. Mero <br />and Willis (1992) used experimental gill nets to obtain monthly samples of walleyes <br />and saugers (Stizostedion canadense) in Lake Sakakawea, North Dakota. Both PSD <br />and RSD-P were highest in spring and fall and lowest during summer samples. We <br />are aware of no work concerning seasonal patterns in size structure for eoldwater <br />fishes. <br />B. GEAR-RELATED BIASES <br />Size-related biases in data also can result from gear selectivity. Reynolds and <br />Simpson (1978) reported that electrofishing was progressively more effective as the <br />length of largemouth bass increased. However, Reynolds (1983) noted that the <br />overestimation was slight when only stock-length (200 mm) fish were- considered. <br />Electrofishing also underestimates the size structure of bluegill (Reynolds and <br />Simpson, 1978) and smallmouth bass (Milewski and Willis, 1991) populations. <br />Laarman and Ryekman (1982) found that trap nets were selective for larger sizes <br />of rock bass (Ambloplites rupestris), walleye, black crappie (Pomoxis nigromaculatus), <br />bluegill, yellow perch (Perca flavescens), and pumpkinseed (Lepomis gibbosus). <br />They did not find significant size selectivity for smallmouth bass and white sucker <br />(Catostomus commersona). <br />Mesh-size selectivity of gill nets causes small fish to be less effectively sampled <br />than larger fish (Hamley, 1975). Thus, size structure is likely overestimated for most <br />fishes that are effectively sampled with gill nets. However, biases in length frequency <br />due to mesh-size efficiency (i.e., the length range of fish effectively sampled by a <br />particular mesh size) of gill nets will vary depending on the complement of mesh <br />sizes chosen to sample a fish population (Willis et al., 1984). <br />Size structure is underestimated for most species of fish collected by cove <br />rotenone sampling (Rayne et al., 1967). However, that bias is probably due to the <br />typical late summer sampling time for the technique. Larger individuals of many <br />species are no longer near shore during Iate summer. Barwick (1984) showed that <br />more representative samples would be collected in May than in August. Bayley and <br />Austen (1988) reported that retrieval efficiencies for marked fish increased with <br />length for both rotenone and detonating cord in ponds and cove enclosures. Thus, <br />the typical underestimation in size structure during cove samples in Late summer is <br />likely due to fish behavior and movement patterns. <br />Use of angler-collected data for making management decisions is becoming <br />more popular and prevalent (Guthrie et ai., 1991). Again, length-related biases must <br />be considered before interpretation of any type of length-frequency data, including <br />stock density indices. Data from bass tournaments are a readily available source of <br />information (Shupe, 1978; Durocher, 1978; Van Rom and Birehfield, 1981; Chapman <br />and Fish, 1983; Duttweiler, 1985; Willis and Hartmann, 1986; Dolman, 1991). <br />Gabelhouse and Willis (1986) found that tournament anglers in Kansas selected for <br />larger sizes of largemouth bass; stock density indices calculated from angler- <br />collected data were overestimated compared to electrofishing samples. Angler <br />diaries also have proven to be a useful technique fox collecting fisheries data (Green <br />eE al., 1984). Ebbers (1987) reported that largemouth bass data supplied by anglers <br />210 <br />
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