Environmental Engineering Reference
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or
f i
f i
1
V j γ ij
C i B =
η j .
(4.91)
j
For the aqueous phase we have
f i
x i w γ i w f i
C i w V w γ i w f i
=
=
(4.92)
or
f i
f i
1
V w γ i w
.
C i w =
(4.93)
f i , we obtain
Now since f i
=
V w γ i w
j
η j
V j γ ij
C i B
C i w =
K Bw =
.
(4.94)
Since the dominant accumulation of hydrophobic solutes in an organism occurs in its
lipid content, we can write
V w
V L
γ i w
γ i L
K BW =
·
· η L ,
(4.95)
where L refers to the lipid phase. Organisms with high lipid content (
η L ) should have
high K BW values.
Since
γ i w is directly proportional to the octanol-water partition coefficient, K ow ,
we can expect an LFER relationship between K BW and K ow . Using the definition of
K ow given previously along with Equation 4.95, we obtain
K ow = η L γ i o
V o
V L
.
K BW
(4.96)
γ i L
For compounds that have similar volume fraction of lipids (
η L ) and similar ratios
of activity coefficients (
γ i w ) , the ratio K BW / K ow should be fairly constant. This
suggests that a linear one-constant correlation should suffice:
γ i o /
log K BW = a log K ow + b .
(4.97)
Such a correlation was tested and confirmed by Mackay (1982). The correlation
developed was for a restricted set of compounds, namely, those with log K ow < 6,
nonionizable, and those with small K B values. The overall fit to the experimental
data was
1.32, r 2
log K BW =
log K ow
=
0.95.
(4.98)
 
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