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McKay, Donald. "Front matter" Multimedia Environmental Models ...

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that the uptake efficiency E A from food in the gastrointestinal tract of a “clean” fish<br />

can also be described by a two-film approach yielding<br />

©2001 CRC Press LLC<br />

1/E A = A WK OW + A O<br />

where A W and A O are water and organic resistance terms similar in principle to t W<br />

and t O, but are dimensionless. A O appears to have a magnitude of about 2, and A W<br />

a magnitude of about 10 –7 , thus, for all but the most hydrophobic chemicals, E A is<br />

about 50%. When K OW exceeds 10 7 , the efficiency drops off, because of a high water<br />

phase resistance in the gut.<br />

A major difficulty is encountered when describing the loss of chemical in feces<br />

and urine. In principle, D values can be defined, but it is quite difficult and messy<br />

to measure G and Z; therefore, neither are known. It is probable that the digestion<br />

process, which removes both mass and lipid content to provide matter and energy<br />

to the fish, reduces both G A and Z A so that D E for egestion is smaller than D A. The<br />

simplest expedient is to postulate that it is reduced by a factor Q, thus we estimate<br />

D E for loss by egestion as D A/Q or D AE/Q, i.e., D E or D EE. The resistances causing<br />

E A for uptake are assumed to apply to loss by egestion. This assumption is probably<br />

erroneous, but it is acceptable for most purposes, especially because there is presently<br />

an insufficiency of data to justify different values for uptake and loss.<br />

The steady-state solution to the differential equation for the entire fish becomes<br />

f F = (D Vf W + D Af A)/(D V + D M + D A/Q)<br />

For the fish inside the epithelium, D A is replaced by D AE.<br />

Assuming that f A equals f W, it is clear that f F will approach f W only when the D V<br />

term dominates in both the numerator and denominator. If K OW is large, e.g., 10 6 ,<br />

the term D A will exceed D V (because Z A will greatly exceed Z W), and the uptake of<br />

chemical in food becomes most important. The fish fugacity then tends toward Qf A<br />

or Qf W, i.e., the fish achieves a biomagnification factor of Q. Q is thus a maximum<br />

biomagnification factor as well as being a ratio of D values.<br />

This biomagnification behavior was first clearly documented in terms of fugacity<br />

by Connolly and Pedersen (1988), Q typically having a value of 3 to 5. Biomagnification<br />

is not immediately obvious until the fugacities are examined instead of the<br />

concentrations. At each step in the food chain, or at each trophic level, there is a<br />

possibility of a fugacity multiple applying. It is thus apparent that fish fugacities<br />

and concentrations are a reflection of a complex combination of kinetic and equilibrium<br />

terms that can in principle be described by D values.<br />

The detailed physiology of the factors controlling Q has been investigated in a<br />

series of elegant experiments by Gobas and colleagues (1993, 1999). The fugacity<br />

change in the gut contents as they journey through the gastrointestinal tract was<br />

followed by head space analysis. These experiments showed convincingly that the<br />

hydrolysis and absorption of lipids reduces the Z value, causing the fugacity to<br />

increase as a result of loss of the lipid “solvent.” Additionally, the mass of food is<br />

reduced, thus G also decreases. The net effect is a decrease in GZ by about a factor<br />

Q of 4. It is noteworthy that Q for mammals and birds is much larger, e.g., 30, thus

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