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Dose Extrapolation Models
Fish Physiologically Based Toxicokinetic Models
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Acknowledgements Gill sub-model pivotal to PBTK for fish
James McKim Russell Erickson John Nichols Melvin Andersen Michael Gargas Harvey Clewell III Alex Hoffman Doug Kuehl Correne Jenson Sharon Bertelsen Partrick Fitzsimmons Frank Whiteman Gill sub-model pivotal to PBTK for fish 1st PBTK model about 1990
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Jim’s Question: “Can fish PBTK models be used to accurately predict uptake, disposition, and elimination of organic chemicals, across routes of uptake and across species? ”
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Rainbow trout Channel Catfish Lake Trout Brook Trout Fathead Minnow Japanese Medaka
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Started with gill exchange
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Lake trout – note lower oxygen consumption
-lower cardiac output Greater fat volume Lower B/W partition coefficient
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Tetra – Penta – Hexa-chloroethane TCE = 2.6 PCE = 3.6 HCE = 4.6 21C
Concentration of three chlorinated ethanes in arterial blood of channel catfish Tetra – Penta – Hexa-chloroethane TCE = 2.6 PCE = 3.6 HCE = 4.6 21C
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Concentration of three chlorinated ethanes in arterial blood of rainbow trout
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Concentration of three chlorinated ethanes in liver of lake trout
Confidence interval for simulation 13 individual simulations SE of the Mean
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Gill uptake in small fish
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FHM ~150mg
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Bioconcentration model for small fish
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TCB logP = 6.0 FHM B/W = Med B/W =
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A = functional gill area – Randall 36% at rest 70% active
Rate constants (L/h) used to predict branchial and cutaneous uptake of TCB Subscript A = functional gill area – Randall 36% at rest 70% active B= total gill area
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Observed and predicted clearance of TCB by Fathead Minnow
Upper limit = total gill area Lower limit = functional
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Red = diffusion in skin Green = blood from skin
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Red – exchange capacity of water to gill
Blue – diffusion in gill Green – blood from gill
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Skin exchange as percent of total vs logP
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Saarikoski 1986 80 mg guppies
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PBTK model for small fish
Carcass – poorly perfused Viscera – richly perfused Balance perfusion – affinity for chemical – shear volume
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Blood binding determining factor
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Large fish skin model Same three compounds
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RBT 1-2% Catfish 3-4%
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Concentration of TCB in contents of stomach ( ) upper intestine ( ) and lower intestine ( )
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Conclusions: PBTK models can be used to accurately predict uptake, elimination, and disposition of organic chemicals in fish. PBTK models can be used to accurately predict dose in fish via branchial, cutaneous and gut uptake. PBTK models can be used to accurately extrapolate dose across fish species.
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