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<br />, <br /> <br />/" <br /> <br /> <br /> <br />ER 2, '(983 <br /> <br />intermediate hosts, Althoug not the ocus fthe present study, other investigators <br />have examined seasonal cha ges in ele s Lake plankton. Anderson and Lenat <br />(1978) and Weiss and Ande son (19 8) eported that copepod densities rose in <br />spring, peaked in mid-sum er, and ined to lowest levels by late fall. Thus, <br />highest numbers of copepod were present during periods of warmest water tem- <br />peratures and when activ cruitment of B. acheilognathi by G, affinis could be <br />demonstrated experime tally, A similar pattern in seasonal dynamics of Both- <br />riocephalus rarus w oted by Jarroll (1979), He observed peak densities of <br />Mesocyclops aterat a time when active recruitment by the definitive host was <br />also occurring. <br />The spatial distributions of copepod intermediate hosts and G, affinis were also <br />considered as potential factors in affecting the population biology of B. acheilo- <br />gnathi, Mesocyclops edax and Cyclops bicuspidatus thomasi are limnetic in dis- <br />tribution, and Tropocyclops prasinus is both littoral and limnetic (Pennak, 1966). <br />Normally, mosquitofish are restricted to the shallow portions of the littoral zone, <br />using vegetation for lateral concealment (Casterlin and Reynolds, 1977). Thus, <br />G, affinis would normally be forced to prey primarily on T. prasinus, However, <br />the absence of piscivorous fishes has permitted G, affinis to expand its lateral <br />spatial distribution significantly in Belews Lake, Indeed, mosquito fish have been <br />collected up to 300 m from shore, at the surface of water 40 m deep. Furthermore, <br />uninfected mosquitofish fed plankton that had been collected 300 m from shore <br />became infected with B. acheilognathi. This observation strongly suggests that <br />transmission of B, acheilognathi is not confined to the littoral zone and that the <br />spatial distribution of copepod intermediate hosts is not a factor affecting the <br />population biology of the cestode in Belews Lake. <br /> <br />OF WASHINGTON, VOLUME 5 <br /> <br /> <br />217 <br /> <br />'- <br /> <br />Acknowledgments <br /> <br />This study was supported, in part, by a grant from the Wake Forest University <br />Research and Publication Fund. We thank Mr. Michael Riggs for allowing us to <br />use some of his unpublished observations on diet preferences of mosquitofish in <br />Belews Lake and for his assistance with the statistical analyses. We appreciate the <br />dialogue with Dr. Glenn Hoffman regarding the taxonomy of B, acheilognathi, <br />as well as the translation of the Dubinina (1982) reference by Dr. Hilda Ching, <br /> <br />Literature Cited <br /> <br />. <br /> <br />Aho, J. M., J. W. Camp, and G. W. Esch. 1982, Long-term studies on the population biology of <br />Diplostomulum scheuringi in a thermally altered reservoir. J. Parasito!. 68:695-708, <br />Anderson, R. M. 1976, Seasonal variation in the population dynamics of Caryophyllaeus laticeps, <br />Parasitology 72:281-305, <br />Anderson, T, P., and D. R. Lenat, 1978, Effects of power-plant operation on the zooplankton <br />community of Belews Lake, North Carolina, In J, H, Thorp and J, W, Gibbons, eds, Energy and <br />Environmental Stress in Aquatic Systems, DOE Symposium Series (Conf-77 I 114), <br />Andrews, C" J. C. Chubb, T, Coles, and A, Dearsley. 1981. The occurrence of Bothriocephalus <br />acheilognathi Yamaguti, 1934 (B, gowkongensis) (Cestoda: Pseudophyllidea) in the British Isles, <br />J, Fish Dis, 4:89-93, <br />Ball, R. L., and R. V. Kilambi. 1973, The feeding ecology of the black and white crappies in Beaver <br />Reservoir, Arkansas, and its effect on the relative abundance of the crappie species, Proc, S,E, <br />Assoc, Game and Fish Comm, 26:577-590, <br />Camp, J. W., J. M, Aho, and G, W. Esch. 1982, A long-term study on various aspects of the <br /> <br />, <br />