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Joint distributional analysis
In this approach, exposure concentrations and effects concentrations are
expressed as distributions. Predicted exposure values are compared to a
distribution of toxicity effects obtained from the literature or from site-specific
information. The overlap in the two distributions can be used to estimate risk
(Suter 1993; USAEWES 1992).
Developing such a model includes the following steps:
failure in a particular fish species) in terms of a test end point (e.g., the
probability of exceeding a relevant effects end point).
b. Obtain the relevant data (i.e., effects data and exposure concentration
data).
c. Calculate the risk that the expected distribution of environmental
concentrations will exceed the distribution of effects concentrations.
This kind of model can be combined with a logistic or binomial model to
evaluate the potential for risk at the population level. However, the appropriate
level of protection must be selected, which is a risk management decision.
Temporal considerations: Potential for recovery of populations
In ecological risk assessments it is desirable to consider how long an
ecosystem may remain degraded after some assault (Suter 1993). Population
levels of some species may recover almost immediately after exposure ceases.
Other species might require longer recovery periods before pre-exposure
population levels are restored. For example, Kennelly (1987) demonstrated that
the removal of adult kelp plants has little effect if it occurs during the time of
year when the plants are reproducing. If, however, plants are removed at other
times of the year, other species may occupy the space and substantially delay the
return of the kelp. Currently, it is not possible to predict the duration of effects
accurately, since the timing, magnitude and order of stresses can cause
unpredictable effects on populations and complicate interpretations of patterns of
competition and predation (Underwood 1989).
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Chapter 5 Uncertainty in Tier IV Risk Assessments
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