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

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The nature of the processes controlling D W and D O is not precisely known, but<br />

it is suspected that they are a combination of flow (GZ) and mass transfer (kAZ)<br />

resistances. If we substitute GZ for each D, recognizing that G may be fictitious,<br />

we obtain<br />

1/k 2 = V FZ F/D V = V FLZ O(1/G WZ W + 1/G OZ O) = (V FL/G W)K OW + (V FL/G O)<br />

= t WK OW + t O<br />

By plotting 1/k 2 against K OW for a series of chemicals taken up by goldfish, Mackay<br />

and Hughes (1984) estimated that t W was about 0.001 hours and t O 300 hours. This<br />

is another example of probing the nature of series or “two-film” resistances using<br />

chemicals of different partition coefficient as discussed in Chapter 7.<br />

The times t W and t O are characteristic of the fish species and vary with fish size<br />

and their metabolic or respiration rate, as discussed by Gobas and Mackay (1989).<br />

The uptake and clearance equilibria and kinetics, i.e., bioconcentration phenomena,<br />

of a conservative chemical in a fish are thus entirely described by K OW, L, t W, and t O.<br />

The bioconcentration equation can be expanded as before to include uptake from<br />

food with a D value D A, loss by egestion (D E) and loss by metabolism (D M), giving<br />

©2001 CRC Press LLC<br />

V FZ Fdf F/dt = D Vf W + D Af A – f F (D V + D M + D E)<br />

A growth dilution D value D G defined as Z FdV F/dt can be included as an additional<br />

loss term. This term can become very important for hydrophobic chemicals<br />

for which the D V and D M terms are small. The primary determinant of concentration<br />

is then how fast the fish can grow and thus dilute the chemical. It should be noted<br />

that this treatment of growth is simplistic in that growth is assumed to be first order<br />

and does not change other D values.<br />

A mass balance envelope problem arises when treating the food uptake or<br />

digestive process. The entire fish, including gut contents, can be treated as a single<br />

compartment. In this case, the food uptake D value is simply the GZ product of the<br />

food consumption rate and its Z value, i.e., G AZ A, subscript A applying to food. Z A<br />

can be estimated as L AZ O, where L A is the lipid content of the food. Often, the<br />

fugacity of a chemical in the food f A will approximate the fugacity in water. The<br />

rate of chemical uptake into the body of the fish is then E AD Af A or D AEf A, where E A<br />

is the uptake efficiency of the chemical. In reality, the gut is “outside” the epithelial<br />

tissue of the fish, and it may be better to treat the fish as only the volume inside the<br />

epithelium. In this case, the uptake D value is G AZ AE A. To avoid confusion, we<br />

define two uptake D values, D AE, which includes the efficiency, and D A, which does<br />

not. The same problem applies to egestion where we define D EE as including a<br />

transport efficiency and D E, which does not.<br />

The digestive process that controls E A and thus D AE is more complicated and<br />

less understood than gill uptake. The first problem is quantifying the uptake efficiency,<br />

i.e., the ratio of quantity of chemical absorbed by the fish to chemical<br />

consumed. It is generally about 50% to 90%. Gobas et al. (1989) have suggested

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