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i. Uncertainties in the toxicity factors due to interspecies extrapolations or
extrapolating from LOAELs to NOAELs.
Identify Clearly All Significant Assumptions
Significant assumptions are those which the risk assessor feels are most critical
to the decision-making process. For example, the selection of a representative
species is a critical element because of the underlying assumption that protection of
the representative species will afford protection of the ecosystem. Therefore, it is
important to be explicit about the importance of this assumption and to present
clearly the justification for making it.
Identify Range, Wherever Possible, the Distribution of
Values a Parameter May Take
For at least each significant assumption, the risk assessor should provide the
range of possible values. For some parameters this information may be available in
the literature (e.g., a range of biota to sediment accumulation factors). For other
assumptions, identifying the range of possibilities may be more difficult. For
example, deciding on a "range" of representative receptors is an exercise in
professional judgement.
Test the Sensitivity of the Risk Assessment
The risk assessment should include a quantitative evaluation of uncertainty, if
possible. Several approaches can be used to characterize uncertainty in parameter
values. When uncertainty is high, bounding estimates should be used. Many of the
models used in the risk assessment are linear. Therefore, a simple sensitivity
analysis should be performed to determine whether the results of the risk analysis
are significantly affected by variations within a range (such as BSF or fish ingestion
rates).
Sensitivity analysis is the process of changing one variable while leaving the
others constant to determine its effect on the output. The results identify those
variables that have the greatest effect on exposure and help focus further
information-gathering activities; they do not indicate the probability of a variable
being at any point within its range. When a single parameter profoundly influences
exposure estimates, the assessor may develop a probabilistic description of its range
(USEPA/ORD 1995). This can be done using site-specific information (such as
creel, market basket, or fish consumption surveys), information in the literature, or
data compiled by USEPA.
The most common example of probabilistic uncertainty analysis is the Monte
Carlo method. This technique assigns a probability density function to each
parameter, then randomly selects values from distributions and inserts them into the
97
Chapter 5 Uncertainty Analysis

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