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<br />63 <br />A <br />B <br />o- <br />so- <br />ae- <br />ao- <br />so- <br />_ ioo-o- <br />S <br />- xao- <br />xao- <br />?E <br />Sao- <br />E Boo- <br />> eoo- <br />loo- <br />eoo- <br />eoo- <br />,ooo- <br />noo- <br />{.e <br />Fig. 2. Size (volume)-frequency distributions expressed as percentage of zooplankters in the Lake Mohave water column (darkened, <br />'_eft) _,^d ,., stomachs of larval razorback sucker from the reservoir (nnPn, rioht)• ± indicates <1%; index of selection, L. indicated <br />where /L/ > about 10 (see text). A. Total zooplankton: water column n = 354 potential food items, larval stomachs n =165 food items. <br />B. Bosmina: water column n =176 potential food items, larval stomachs n =149 food items. <br />to and largely a function of their primary food, <br />Bosmina (Fig. 2B). <br />Arizona Bay Backwater <br />Razorback sucker larvae were first captured from <br />the Arizona Bay backwater on 7 March, 5 to 8 <br />weeks after adults were stocked. Numbers in- <br />creased quickly and remained high into April. <br />Mean TL of backwater larvae (n = 367) was ini- <br />tially similar to that of Lake Mohave fish (approx- <br />imately 10 mm), but increased to >16 mm by late <br />April when the largest specimen was 20.3 mm, <br />similar in size to that achieved by hatchery-reared <br />razorback in comparable time (Papoulias unpubl. <br />data). Larvae in the backwater thus survived to <br />grow nearly twice the size (middle postlarvae) of <br />the largest (early postlarvae) wild individuals from <br />the reservoir. <br />Zooplankton species richness was greater in the <br />backwater than in the reservoir, but the most abun- <br />dant kinds were the same in both places (Table 2). <br />Rotifers were relatively more numerous (more <br />than 50%) and copepods less abundant in the back- <br />water (Table 1). Total zooplankton density aver- <br />aged 377 animals m-3, only about 25% that of the <br />reservoir. <br />Predominant foods of sucker larvae in the back- <br />water included rotifers, cladocerans (Bosmina, <br />Ceriodaphnia, and Daphnia) and copepods (Table <br />2). Dietary diversity was greater than in the reser- <br />voir, and included individual animals of larger size <br />(e.g., larval Chironomidae and Trichoptera). <br />However, we found no evidence that mean size of <br />ingested food increased as fish TL increased from <br /><12 mm to ---20 mm. Backwater larvae showed <br />positive selection for cladocerans (especially <br />Bosmina) and strong negative selection for rotifers <br />(Table 1). <br />Among available foods, backwater larvae ex- <br />hibited positive selection for zooplankters 50 to <br />399 x 10-4 mm3 and negative selection for those 10 <br />to 14 x 10-4 mm3 (Fig. 3a). Positive selection was <br />strongest for rotifers 25-29, Daphnia 100-299 and <br />1,000--4,999, and copepods 100-299 x 10-' mm', <br />while strongest negative selection was for rotifers <br />10-14, Bosmina 100-199, and Daphnia 5,000- <br />14,999 x 10-4 mm3 (Figs. 3b-e). <br />Discussion <br />Zooplankton communities and larval razorback <br />sucker diets were similar in Lake Mohave and in