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Chaoborus

Apperson, C.S., C.H. Schaefer, A.E. Colwell, G.H. Werner, N.L. Anderson, E.F. Dupras, Jr., and D.R. Longanecker. 1978. Effects of diflubenzuron on Chaoborus astictopus and nontarget organisms and persistence of diflubenzuron in lentic habitats. Jour. Econ. Entomol. 71 521-527. [Pg.1017]

Hare, L. and Tessier, A. (1998). The aquatic insect Chaoborus as a biomonitor of trace metals in lakes, Limnol. Oceanogr., 43, 1850-1859. [Pg.202]

Inhibited adult emergence by 95-100% of a gnat (Chaoborus astictopus), 2-7 days after treatment. Crustacean zooplankton suppressed at all treatment levels, especially cladocerans and copepods. Rotifers and algae were not affected. Bluegills that fed predominantly on cladocerans and copepods switched to chironomid midges and terrestrial insects after treatment, with no adverse effects... [Pg.1006]

Figure 3. Reconstructions of (A) diatom-based and (B) chrysophyte-based monomeric Al for Big Moose Lake, and diatom-based monomeric Al for (C) Deep Lake, (D) Upper Wallface Pond, and (E) Windfall Pond in the Adirondack Mountains, New York. Reconstructions are bounded by bootstrapping estimates of the root mean-squared error of prediction for each sample. Bars to the right of each reconstruction indicate historical (H) and Chaoborus-based (C) reconstructions of fishery resources. The historical fish records are not continuous, unlike the paleolimnological records. Intervals older than 1884 are dated by extrapolation. (Reproduced with permission from reference 10. Figure 3. Reconstructions of (A) diatom-based and (B) chrysophyte-based monomeric Al for Big Moose Lake, and diatom-based monomeric Al for (C) Deep Lake, (D) Upper Wallface Pond, and (E) Windfall Pond in the Adirondack Mountains, New York. Reconstructions are bounded by bootstrapping estimates of the root mean-squared error of prediction for each sample. Bars to the right of each reconstruction indicate historical (H) and Chaoborus-based (C) reconstructions of fishery resources. The historical fish records are not continuous, unlike the paleolimnological records. Intervals older than 1884 are dated by extrapolation. (Reproduced with permission from reference 10.
Havas, M. and Likens, G.E. (1985) Toxicity of aluminum and hydrogen ions to Daphnia catawba, Holopedium gibberum, Chaoborus punctipennis, and Chironomus anthrocinus from Mirror Lake, New Hampshire, Canadian Journal of Zoology 63 (5), 1114-1119. [Pg.48]

L.A. Giguere, R.L. Dunbrack (1990). Thin layer interference may reduce the visibility of transparent phantom midge [Chaoborus trivittatus) to predators. Can. J. Fish. Aquat. Set, 47,1043-1046. [Pg.478]

Dodson, S.I., T. Hanazato, and P.R. Gorski. 1995. Behavioural responses of Daphnia pulex exposed to carbaryl and Chaoborus kairomone. Environ. Toxicol. Chem. 14 43-50. [Pg.768]

Harvell CD (1990) The ecology and evolution of inducible defenses. Q Rev Biol 65 323-340 Havel JE, Dodson SI (1984) Chaoborus predation on typical and spined morphs of Daphniapulex ... [Pg.368]

Spitze K (1992) Predator-mediated plasticity of prey life history and morphology Chaoborus americanus predation on Daphnia pulex. Am Nat 139 229-247... [Pg.370]

Ponton DE, Hare L (2010) Nickel dynamics in the lakewater metal biomonitor Chaoborus. Aquat... [Pg.121]

See other pages where Chaoborus is mentioned: [Pg.1006]    [Pg.1137]    [Pg.142]    [Pg.1137]    [Pg.123]    [Pg.208]    [Pg.85]    [Pg.546]    [Pg.467]    [Pg.240]    [Pg.57]    [Pg.75]    [Pg.415]    [Pg.418]    [Pg.335]    [Pg.361]    [Pg.523]    [Pg.505]    [Pg.937]    [Pg.115]   
See also in sourсe #XX -- [ Pg.1136 ]

See also in sourсe #XX -- [ Pg.1136 ]

See also in sourсe #XX -- [ Pg.85 ]

See also in sourсe #XX -- [ Pg.240 ]

See also in sourсe #XX -- [ Pg.30 , Pg.48 ]

See also in sourсe #XX -- [ Pg.415 , Pg.418 ]



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Chaoborus astictopus

Chaoborus sp.

Midge Chaoborus

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