Page 691 - The Toxicology of Fishes
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Fish Toxicity Studies                                                       671


                                         144

                                         120

                                         96
                                        LT50 (hr)  72  incipient lethal concentration (LC50)
                                                         Time-independent threshold or

                                         48

                                         24

                                          0
                                           100       150        200       250        300
                                                    Exposure Concentration (µg/L or ppb)
                                                                 C
                                        0.010


                                        0.008
                                      1/LC50 (µg/L)  0.006  incipient lethal concentration (LC50)

                                                       Time-independent threshold or
                                        0.004


                                        0.002

                                        0.000
                                            0     25     50     75    100    125   150
                                                          Exposure Time (hr)
                                                                D
                       FIGURE 15.4 (cont.) (C) Plot of LT 50  (median time to death) vs. exposure concentration (LT 50  values from part A). (D)
                       Plot of the inverse of LC 50  vs. exposure time (LC 50  values for low-fat fish exposed to pentachlorphenol). (From van den
                       Heuvel, M.R. et al., Aquat. Toxicol., 20, 235–252, 1991. With permission.)


                       of organisms (fish, invertebrates, algae). The utility of single-species fish tests is a function of the criteria
                       used to select test organisms (see below). The main limitation is that effects in the laboratory may not
                       occur at all or to the same degree at similar concentrations in the environment. Effects measured in the
                       laboratory are a result of the inherent variability of the test fish population under constant conditions.
                       Furthermore, bioavailability of chemicals is optimized because filtered laboratory waters are used instead
                       of natural waters. These tests do not consider species interactions and environmental influences. Because
                       most tests are conducted with water exposures, sediment and food exposures are rarely considered. The
                       latter exposure routes become particularly relevant with chemicals that are hydrophobic.
                        Small simulated model microcosm tests can also be conducted in the laboratory using a multispecies
                       approach. Laboratory microcosms are small-scale enclosures (e.g., fiberglass, glass, plastic) containing
                       a multitude of samples (e.g., water, sediment, one or more species of fish, invertebrates, and plants).
                       Any combination or all of the latter samples may be incorporated into the test depending on study
                       objectives. The advantage of this approach is that effects beyond the level of direct effects on a single
                       species can be studied, including indirect effects. Results provide information more predictive of the
                       ecological consequences of chemical release; however, environmental conditions are still controlled in
                       laboratory microcosms but replication may be easily obtained. Although cause-and-effect relationships
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