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Ceriodaphnia

Kubitz, J.A., E.C. Lewek, J.M. Besser, J.B. Drake III, and J.P. Giesy. 1995. Effects of copper-contaminated sediments on Hyalella azteca, Daphnia magna, and Ceriodaphnia dubia survival, growth, and enzyme inhibition. Arch. Environ. Contam. Toxicol. 29 97-103. [Pg.224]

Schubauer-Berigan, M.K., J.R. Dierkes, PH. Monson, and G.T. Ankley. 1993. pH-dependent toxicity of Cd, Cu, Ni, Pb, and Zn to Ceriodaphnia dubia, Pimephales promelas, Hyalella azteca and Lumbricus variegatus. Environ. Toxicol. Chem. 12 1261-1266. [Pg.230]

Winner, R.W. and H.A. Owen. 1991. Toxicity of copper to Chlamydomonas reinhardtii (Chlorophyceae) and Ceriodaphnia dubia (Crustacea) in relation to changes in water chemistry of a freshwater pond. Aquat. Toxicol. 21 157-170. [Pg.234]

Ceriodaphnia reticulata Hermit crab, Clibanarius olivaceous ... [Pg.690]

Cladoceran, Ceriodaphnia dubia Daphnid, Daphnia magna 0.5 14... [Pg.968]

After first treatment, reduction within 1 week of 3 species of cladocerans (Daphnia laevis, Ceriodaphnia sp., Bosmina longirostus sp.), and 2 species of copepods (Cyclops sp., Diaptomus sp.). No recovery of Daphnia and Ceriodaphnia for 6 months, but Bosmina reappeared 11 weeks later. Diaptomus was depleted for 4 months, but Cyclops recovered in 6-7 weeks. The amphipod Hyallela azteca was eliminated within 4 weeks, and no recolonization was evident after 6 months. No adverse effects on oligochaetes, snails (Physa sp.), or ostracods (Cyprodopsis sp.). After second treatment, temporary reduction in Cyclops and Bosmina, and no significant effects on ostracods, snails, or worms... [Pg.1006]

Cladoceran, Ceriodaphnia lacustris 0.01 pg/L Filtration rate of alga (Chlamydomonas 6... [Pg.1109]

Ceriodaphnia reticulata 4.1 Reduction in number of young/female in lifetime exposure 4... [Pg.1207]

Invertebrate species have been widely used in toxicity studies of pesticides [61]. Zooplankton play a key role in the food chain because they occupy a central position. Therefore, their responses to natural and anthropogenic stresses are intimately linked with other food predator organisms. The most widely accepted bioassays employ species such as Ceriodaphnia dubia, Daphnia magna, Artemia salina, or Thamnocephalus platyurus [62-64]. D. magna has been used for many years as a standard aquatic test species and formally endorsed by the major international organizations such as the EEC, OECD, and ASTM [65-67]. Its choice is mainly because it represents the zooplankton community and is a species of worldwide occurrence. In addition, it has a greater sensitivity to toxicants, particularly pesticides, compared with other aquatic species [61,68] (Table 1). [Pg.66]

Bitton, G., Rhodes, K., and Koopman, B. Ceriofast an acute toxicity test based on Ceriodaphnia dubia feeding behavior. Environ. Toxicol. Chem., 15(2) 123-125,1996. [Pg.1633]

In addition to acute toxicity tests, two standard chronic toxicity test methods are widely accepted by various regulatory agencies the seven-day Ceriodaphnia survival and reproduction test and the 21-day Daphnia reproduction test. [Pg.24]

Cowgill, U.M. Keating, K.I. Takahashi, l.T. Fecundity and longevity of Ceriodaphnia dubia/ affinis in relation to diet at two different temperaffires. J. Crustacean Biol. 1985, 5, 420-429. [Pg.55]

American Society for Testing and Materials (ASTM). Standard guide for conducting three-brood, renewal toxicity tests with Ceriodaphnia dubia. In Annual Book of ASTM Standards ASTM Philadelphia, 1989 Vol. 11.04, 360-379. [Pg.55]


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See also in sourсe #XX -- [ Pg.1003 ]

See also in sourсe #XX -- [ Pg.1003 ]

See also in sourсe #XX -- [ Pg.300 ]




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Ceriodaphnia dubia

Ceriodaphnia lacustris

Ceriodaphnia reticulata

Cladoceran Ceriodaphnia

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