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average total PCB concentration in the sediments from the proposed dredging
project area is 1ug total PCB /g sediment.
in sediments at the reference site is 0.10 ug total PCB/g. The assessment assumes
that this is the exposure point concentration for winter flounder when foraging
away from the site and its area of influence.
The average fraction lipid of a flounder is 0.1, based on hypothetical data
provided by a fisheries agency.
Therefore, the average sediment exposure concentration of total PCB, Cs, at
the disposal site is:
(1 H 0.5) + (0.1 H 0.5) = 0.55 ug total PCB/g sediment
Cs
=
The state has also supplied data indicating that the fraction organic carbon in
sediments in the area is 0.05 (5 percent).
A locally calculated biota sediment accumulation factor (BSAF) is 3, based
on USEPA studies of PCB in flounder and sediment in this bay. The projected
body burden (weight wet), Ca, to a flounder exposed to this total PCB
concentration in sediments of 5 percent organic carbon is:
(0.55/Foc) H BSAF H (Fl)
Ca
=
(0.55/.05) H 3 H 0.1
=
=
3.3 ug total PCB/g wet weight flounder tissue
This body burden value can be used in both human health and ecological risk
assessments.
This example could have used a different species such as lobster. In that case,
the general method would remain the same, but parameters such as foraging area,
bioaccumulation factor, and fraction lipid would differ. Also, the example is
relatively simple in that it does not address differential uptake and storage of
PCB congeners among tissues. In some instances, it may be important to estimate
uptake in organs other than muscle. For example, lobster hepatopancreas has a
different fraction lipid than lobster muscle. In a human health risk assessment,
where some individuals in a population may consume the hepatopancreas, it
becomes important to calculate a separate concentration for that tissue based on
its particular lipid content.
F10
Appendix F Hypothetical Example
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