Trout stocking in the mid-1960s eliminated the calanoid copepod Hesperodiaptomus arcticus and other largebodied crustaceans such as Gammarus lacustris, Daphnia middendorffiana, and Daphnia pulex from many alpine lakes in the Rocky Mountain Parks of Canada. H. arcticus frequently dominates the plankton communities of fishless lakes, preying on rotifers and nauplius larvae. Following the extirpation of H. arcticus, rotifers and small-bodied cyclopoid copepods dominate the zooplankton assemblages of alpine lakes.We studied the zooplankton community of Snowflake Lake, Banff National Park, from 1966 to 1995. H. arcticus was eliminated following stocking of the lake with trout in the 1960s. It failed to become reestablished after the disappearance of the fish population in the mid-1980s. Several species of rotifers and small-bodied crustaceans, species originally rare or absent from the plankton, became abundant following fish stocking and remained so after the fish population declined.In 1992, we reintroduced H. arcticus to Snowflake Lake. The H. arcticus population grew exponentially for 4 yr, but had not reached stable densities typical of unmanipulated alpine lakes by 1995. By 1994, however, even the small population of Hesperodiaptomus was beginning to suppress populations of rotifers, copepod nauplii, and large diatoms. Because H. arcticus is omnivorous, a simple model of cascading trophic interactions did not predict the outcome of trophic manipulations in this alpine lake.

The predaceous cladoceran Leptodora kindti (Focke) became established in Third Sister Lake, Michigan, after individuals escaped from experimental enclosures in 1987. By 1988, the Leptodora population exhibited seasonal dynamics characteristic of natural populations. The maximum seasonal abundance of Leptodora increased to 85 individuals m Ϫ3 3 yr following the introduction. After the appearance of Leptodora, small-bodied cladocerans (Ceriodaphnia and Bosmina) virtually disappeared from the lake. There were strong seasonal shifts in the dominance patterns of both cladocerans and copepods, and Daphnia species diversity increased. Results from this unplanned introduction suggest that invertebrate predators can have a rapid and lasting effect on prey populations, even in the presence of planktivorous fish. Small-scale (Ͻ20 km) geographic barriers might be as important as large-scale barriers to dispersal of planktonic animals.Both planktivorous fish and invertebrate predators have the potential to structure crustacean zooplankton communities through size selective predation. Planktivorous fish that feed visually select the largest available prey while invertebrate predators remove smaller individuals (Zaret 1980). Whereas the effects of planktivorous fish on zooplankton community structure are well established (Brooks and Dodson 1965;Hall et al. 1976), the effects of invertebrate predators are less clear. Large predatory zooplankton, such as Chaoborus and certain calanoid copepods (e.g., Hesperodiaptomus, Heterocope), are often abundant in the absence of fish and can inflict considerable mortality on populations of small-bodied prey (Von Ende and Dempsey 1981;Luecke and O'Brien 1983;Elser et al. 1987;McNaught et al. 1999). Such intense predation can lead to the exclusion of smallbodied species, thereby changing the size structure of the zooplankton community (Dodson 1974;Luecke and O'Brien 1983;Black and Hairston 1988;Hanazato and Yasuno 1989). When fish are present, large nonmigratory inverte-

Aquatic prey species respond to predators with fast (developmental) and slow (selective) feedbacks. Natural selection is assumed to fashion details of induction and to modify baseline morphology, but only rarely do we catch the slower (multi-generation) process in action. Laboratory experiments with Bosmina detected predatormediated induction and estimated spine heritability (h 2 5 0.2-0.5). Third Sister Lake, Michigan, U.S.A., Bosmina exhibited induction to resident (Mesocyclops) and to two nonresident, neighborhood predators (Epischura and Leptodora). However, the magnitude of induction in Third Sister Lake Bosmina to nonresident predators (Epischura, Leptodora) was muted, when compared with induction and final spine lengths in Epischura-Leptodora lakes. Inadvertent escape of Leptodora into Third Sister Lake in 1987 created a long-term (multiyear), whole-lake experiment, where resident Bosmina populations fell under intense size selection. During the interval, Leptodora suppressed a late-season smaller, short-featured species (B. freyii), favored seasonal expansion of an overwintering long-featured species (B. liederi), and selected for longer features in the latter species. Before local extinction, defensive spines of B. liederi achieved lengths comparable to populations that co-occur with Epischura and Leptodora.

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