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352 <br />PAPOULIAS AND MINCKLEY <br />1 <br />•0 <br />0 <br />A <br />-1 <br />t <br />0 <br />B <br />-1 <br />1 <br />J • <br />0 C) <br />- -1 <br />U t <br />aI <br />a? <br />U, 0 O <br />X D0• 0 Oo <br />-t <br />_C I <br />•L <br />O 0 <br />d 0 G C) <br />J E o0 <br />-1 <br />1 <br />0 0 <br />F <br />-t <br />1 <br />0 <br />G <br />-t <br />9 14 19 i4'29 <br />Total fish length (mm) <br />FIGURE 7.-Prey species selection by variously sized <br />razorback sucker larvae reared in ponds at Dexter Na- <br />tional Fish Hatchery, New Mexico, 1985, as indicated <br />by the linear index of selectivity (L;) of Strauss (1979). <br />(A) rotifers, (B) chironomids, (C) cladocerans, (D) as- <br />tracods, (E) nauplii, (F) invertebrate eggs, and (G) cope- <br />pods. Positive (negative) numbers indicate organisms <br />were more (less) numerous in guts of larvae than in pond. <br />Closed circles indicate significant differences from zero. <br />wood Basin (Langhorst and Marsh 1986). Zoo- <br />plankton densities nonetheless remain low. In <br />1982, for example, they varied from 27.3 to 44.6 <br />organisms/L in the same areas and times of year <br />when razorback sucker larvae were present (L. J. <br />Paulson, University of Nevada, Las Vegas, per- <br />sonal communication). In 1985, densities aver- <br />aged only 1.5 organisms/L at the same places lar- <br />vae were caught. Densities in a cutoff bay inhabited <br />by larvae were even lower, averaging less than 0.5 <br />potential food items per liter in six samples (Marsh <br />and Langhorst 1988). <br />Wild-caught larvae averaged 10.6 mm TL in <br />i <br />0 <br />0.1 mm <br />-t <br />J 1 <br />_T <br />0 <br />U <br />0.2 mm <br />rn -1 <br />1 <br />O <br />X <br />? o <br />C <br />0 0.3 mm <br />N -1 <br />J <br />0 <br />0.4 mm <br />9 14 19 24 29 <br />Total fish length (mm) <br />FIGURE 8. -Prey-size selection (as body width) by var- <br />iously sized razorback sucker larvae reared in ponds at <br />Dexter National Fish Hatchery, New Mexico, 1985, as <br />indicated by the linear index of selectivity (L;) of Strauss <br />(1979). Positive (negative) numbers indicate organisms <br />were more (less) numerous in guts of larvae than in pond. <br />Closed circles indicate significant differences from zero. <br />Lake Mohave in 1985, and no growth was re- <br />corded although the larvae were present from Feb- <br />ruary through April (Marsh and Langhorst 1988). <br />Ages of these larvae were unknown, but larvae of <br />comparable sizes in ponds at Dexter National Fish <br />Hatchery were 14-21 d old (posthatch) in high- <br />fertilization treatments at invertebrate densities of <br />43.3/L, and 21-28 d old in unfertilized ponds at <br />12.5 organisms/L. In the cutoff bay where zoo- <br />plankton density was less than 0.5/L, larvae grew <br />to a mean TL of about 16.0 mm in 69 d. Larvae <br />at Dexter achieved 16.0 mm TL in unfertilized <br />ponds 49 d from hatching. In the laboratory, lar- <br />vae grew to 16.0 mm in 57 d at densities of 50 <br />Artemia nauplii/L (Papoulias and Minckley 1990). <br />Perhaps larval density in the bay was low and (if <br />razorback sucker larvae are efficient hunters, as <br />suggested above) the larvae found enough food to <br />survive and grow. The slightly slower growth to <br />16.0 mm compared with that at Dexter (69 versus <br />49 d) may support this possibility. <br />Papoulias and Minckley (1990) concluded that <br />razorback sucker larvae reared in the laboratory