13.07.2015 Views

Advances in Water Treatment and Enviromental Management

Advances in Water Treatment and Enviromental Management

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CONTROL OF DANGEROUS SUBSTANCES IN UK SURFACE WATERS 47Figure 1. Schematic flow chart for the derivation of environmental quality st<strong>and</strong>ards.between the effects of the particular compound <strong>and</strong> those of other potentiallytoxic compounds present. It is important to compare the tentative EQSwith the highest observed concentration which has no effect on theecosystem, rather than with the lowest concentration which does have aneffect. Any discrepancies between the field data <strong>and</strong> the tentative EQS requirethe reassessment of the available field <strong>and</strong> laboratory data <strong>and</strong>, if necessary,the application of a different safety factor.The sett<strong>in</strong>g of EQS values relies heavily on knowledge of bioaccumulation<strong>and</strong> toxicity effects. This <strong>in</strong>formation is often <strong>in</strong>complete <strong>and</strong> depends on<strong>in</strong>terpretation. The field data are often <strong>in</strong>adequate, especially for the lessfrequently occurr<strong>in</strong>g organic compounds, to verify the tentative EQS derivedfrom the laboratory data. The application of safety factors must thereforetake account of the different toxicities <strong>and</strong> actions of the chemicals on thetarget organisms <strong>and</strong> the quality of the toxicity data available.When deriv<strong>in</strong>g EQS values for substances which are designed for a specificpurpose, such as pesticides, it is particularly important that toxicity testsare available for the target species as the sensitivities of different taxonomicgroups to these compounds vary widely.

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