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acceptable level of animal bioaccumulation. Although statistical significance, per
se, cannot indicate environmental importance, a statistically significant increase
above reference bioaccumulation has been considered in the OTM and ITM to
indicate a potential for effects, and that convention is followed in the Tier II and
III animal bioaccumulation in the UTM. Detailed decision guidance is provided
in the discussions of each of the tiers.
8.1.3 Data Requirements
The evaluation of animal bioaccumulation requires information on the CDF
and its environmental setting, the planned dredged material management, and the
characteristics of the dredged material. Much of this comes from the available
information compiled in Tier I, and supplemented (if necessary) by the Tier II and
Tier III test data.
8.1.4 Summary of Tiered Evaluation of Animal Bioaccumulation
A flowchart illustrating the tiered evaluation for animal uptake is shown in
Figure 8-1. The other contaminant mobility pathways addressed in the UTM are
evaluated primarily on the basis of standards or criteria, and risk assessment plays
a relatively minor role in Tiers I through III. In the absence of technically
applicable standards or criteria, animal (and plant) bioaccumulation evaluations in
the UTM rely more directly on risk assessment in Tiers I through III. Evaluation
of all pathways relies on risk assessment in Tier IV.
The risk-based approach to evaluation of animal bioaccumulation is structured
around the conceptual site model developed in Tier I. The conceptual site model
provides the framework and the context for conducting the evaluation (Cura,
Wickwire, and McArlde in preparation). It describes the dredged material
management planned, the environmental setting of the site, and how the planned
site management interacts with the environmental setting to determine what
effects might potentially occur. The evaluation in Tiers I through III emphasizes
three components evaluated in the context of the conceptual site model:
Populations of receptors of concern (ROC) outside the CDF, discussed in
Section 2.2.3
Constituents of concern (COC), discussed in Sections 2.2.2 and 3.4
Complete exposure routes, discussed in Section 2.2.4. Identification of
reasonable complete exposure routes by which ROC populations outside
the CDF can come into direct physiological contact with COC is key to
the entire evaluation. If there are no reasonable complete exposure
routes, there can be no exposure and thus no effect or risk.
8-3
Chapter 8
Animal Bioaccumulation
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