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Toxicology of Industrial Compounds

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N.FEDTKE 173<br />

were developed that describe the uptake, metabolism and disposition <strong>of</strong> BE<br />

and BAA (Johanson, 1986; Corley et al., 1993, 1994; Shyr et al., 1993).<br />

The model <strong>of</strong> Corley et al. (1993, 1994) is a refinement <strong>of</strong> Johanson’s<br />

model (1986) and consists <strong>of</strong> two submodels. The first submodel describes<br />

the uptake and disposition <strong>of</strong> BE and consists <strong>of</strong> the tissue compartments<br />

rapidly perfused organs, slowly perfused organs, fat, skin, muscle,<br />

gastrointestinal tract, and liver as the metabolizing tissue. The BE<br />

submodel allows uptake via the inhalation and dermal routes and in<br />

addition provides the possibility <strong>of</strong> uptake via IV infusion and the<br />

gastrointestinal tract in order to validate the model with laboratory data.<br />

The second submodel tracks the disposition <strong>of</strong> BAA in the same tissue<br />

compartments, but the kidney was removed from the rapidly perfused<br />

organs as separate tissue to allow for the excretion <strong>of</strong> BAA metabolites.<br />

The two submodels are linked together by the metabolism <strong>of</strong> BE to BAA<br />

via a saturable enzymatic pathway catalyzed by alcohol and aldehyde<br />

dehydrogenases in the liver. Competing pathways (BE conjugation and<br />

BE O-dealkylation) are lumped together and described by an additional<br />

enzymatic pathway with Michaelis-Menten kinetics. The model assumes<br />

that BAA is bound to proteins in blood and is eliminated by a saturable<br />

process in the kidneys. The rate <strong>of</strong> BAA elimination by the kidneys is<br />

described as the sum <strong>of</strong> glomerular filtration rate <strong>of</strong> BAA and the acid<br />

transport <strong>of</strong> BAA assuming that no reabsorption occurs. The biochemical<br />

constants determined experimentally in the rat were scaled to humans by<br />

(body weight) 0.7 . In the validation process, the model successfully described<br />

a wide variety <strong>of</strong> rat and human data from different laboratories using<br />

several routes <strong>of</strong> administration.<br />

BAA was predicted to be formed more rapidly in rats compared with<br />

humans, but to be eliminated slower in humans than in rats. In summary,<br />

higher maximum concentrations <strong>of</strong> BAA in blood (C max) and also higher<br />

areas under the BAA concentration-time curves (AUC) were predicted for<br />

rats than for humans, especially as the vapour concentration was<br />

increased. For the purpose <strong>of</strong> dose-response and interspecies extrapolation,<br />

BAA-C max and BAA-AUC were used as estimates <strong>of</strong> the internal dose<br />

surrogate; C max can be related directly to the in vitro haemolysis studies<br />

with BAA and is responsive to the dose-rate. The in vitro studies performed<br />

(Bartnik et al., 1987; Ghanayem et al., 1987; Ghanayem, 1989; Udden,<br />

1994; Udden and Patton, 1994) suggest that approximately 0.2 mM BAA<br />

is required to produce slight haemolysis <strong>of</strong> rat red blood cells. At about 2<br />

mM BAA nearly complete haemolysis was observed. The model predicts<br />

for nose-only exposure that these concentrations are reached in the rat at<br />

BE exposure concentrations <strong>of</strong> about 100 ppm and 800 ppm for 6 h,<br />

respectively, which is consistent with observations in vivo (Tyler, 1984;<br />

Sabourin et al., 1992).

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