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the water during placement. The area is a low-to-moderate energy environment,
has a seasonal thermocline (indicating little surface to bottom mixing during
summer), and is generally depositional. There is some potential for resuspension
of the sediments and advection through wave or storm action and during winter
with the breakdown of the seasonal thermocline. There is also potential for
diffusion from pore water and advection offsite. These mechanisms could bring
the potential COCs into contact with receptors.
Description of Complete Exposure Pathways
The risk assessor used the following questions to guide the determination of
complete exposure pathways between the proposed dredged material and the
potential receptors:
b. Are one or more receptors inhabiting or using an area where
contamination exists or will exist?
contact it currently or in the future?
d. Are there advective or dispersive processes which may deliver the
contaminant to a receptor or habitat?
f. Is contamination bioaccumulative or bioconcentratable?
g. Are there higher-order predators which may accumulate the
contaminant?
present at surface sediments?
k. Can contaminants be leached or eroded from surface sediments or soil?
The answers to these questions indicate that there is a benthic community
with potential for direct contact and ingestion of sediments by invertebrate
organisms at the management area. There is then potential for bioaccumulation to
higher-order predators through ingestion of the benthic organisms. There is some
potential for bioconcentration of COCs from suspended sediments in the water
column to forage fish and zooplankton, given the moderate vertical mixing which
may occur at the site in winter. The management option does not have an effluent
discharge, so there is minimal likelihood of dissolved contamination in the water
column (there is a potential for exposure in the water column during disposal, but
F5
Appendix F Hypothetical Example
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