physiologically based pharmacokinetics – lecture ii melvin andersen ciit centers for health...
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Physiologically Based Pharmacokinetics – Lecture
II
Melvin AndersenMelvin AndersenCIIT Centers for Health ResearchCIIT Centers for Health Research
October 27, 2006October 27, 2006University of North CarolinaUniversity of North Carolina
I. PBPK Models for the Metabolism of Methylene Chloride and Application in Risk Assessment - EasyEasy
II. Thinking about Pharmacokinetics while thinking more deeply about terms such as exposure and mixture? - HarderHarder
TODAY’S TOPICSTODAY’S TOPICS
StainlessSteel
BellowsPump
~ 2.0L/min
CO2
Scrubber
ParticulateFilter
O2 Monitor
PressureGauge
InjectionPort
Ice Filled Pan forH2O Condensation
Desiccator JarChamber
~ 100 mL/min
INTEGRATOR
Gas Chromatograph
5 mL GasSampling Loop
Gas Uptake and Metabolic Parameters
Vial equilibration and Partitioning
Experiments to Get Some of the Experiments to Get Some of the Needed Parameters for a PBPK Needed Parameters for a PBPK ModelModel
Chamber Volume
Alveolar Space
Lung Blood
Fat Tissue Group
Muscle TissueGroup
Richly PerfusedTissue Group
LiverMetabolizingTissue Group( )
MetabolitesVmax
Km
Cart
Ql
Cart
Qr
Cart
Qm
Cart
Qt
Cart
Qc
Calv (Cart/Pb)
QalvQalv
Cinh
Qc
Cven
Cvt
Cvm
Cvr
Cvl
kf
Adding a Different Exposure ScenarioAdding a Different Exposure Scenario
Gas Uptake Methods Estimate Metabolic Parameters: – Vmax and Km- kf
Ch
am
ber
loss
wit
h C
H2B
rCl
Saturable process
Linear process
Motivation for Studying Bromide
– We studied bromide concentrations in plasma after 4-hr exposures of rats to dibromomethane at various concentrations.
– From data, determined production rates of bromide ion during exposure and thereby estimated biochemical constants (Vmax and Km and kfc) for metabolism of CH2Br2 or CH2BCl in rats.
– Examine the effect of inducers and inhibitors on bromide production curves to see if we can discover the biochemical pathways of dihalomethane metabolism.
Formation and Distribution of Bromide from Oxidation of Dibromomethane
A complete distributional model for CH2Br2 with hepatic metabolism via Cytochrome P450 2E1 oxidation and GST.
kf
Plasma inorganic bromide concentrations on ambient concentrations of CH2BrCl following 4-hr exposures using naive, 2,3-EP, and pyrazole-pretreated rats. The smooth curves were generated by the PBPK.
• 2,3-EP reduces liver GSH
• Pyrazole blocks microsomal oxidation
HbCO concentrations in naïve, 2,3-EP-, and pyrazole-pretreated animals following 4-hr exposures to CH2BrCl.
What about carbon monoxide?
METHYLENE CHLORIDE - 1987
• Causes cancer in mouse lung and mouse liver by inhalation, but not in mice exposed via drinking water.
• Metabolized by two pathways, each producing a reactive metabolite. Oxidation to formyl chloride and GST-conjugation to chloromethylglutathione
• Either pathway could produce a mutagenic metabolite. Which is it?
H
H Cl
Cl
rate
exposure level - PPM
G SH
CYP 2E 1
METHYLENE CHLO RIDE METABOLISM:
C H2C l2 C l-C -H
O C Y P 2E1
GST
G S -CH Cl
ReactionPathw ays
Reaction Kinetics
1000
METHYLENE CHLORIDE - 1987 H
H Cl
Cl
The two pathways contribute differentially at high and low exposure concentrations in rodents, as noted in studies with bromide release.
METHYLENE CHLORIDE - 1987
Responses related to intensity of tissue exposure to short-lived, spontaneously reactive intermediates.
Dose metric for PBPK modeling was estimated by
(amount metabolite formed )/tissue volume/time
Evaluate relationship between daily tissue exposure and cancer in the two-year mouse bioassay.
Provide an approach to extrapolate to lower doses, dose routes, and between mouse and humans.
H
H Cl
Cl
PBPK Model Structure for Methylene Chloride
Attributes:
- Tissue Volumes - Blood Flows - Partition Coefficients - Metabolic Constants - Breathing Rate - Water Intake - Tissue metabolism
H
H Cl
Cl
Lung GasExchange
Lung TissueQC·CV
QP·CI QP·CX
QC·CA
GSTMFO
Richly PerfusedTissues
QR·CAQR·CVR
Slowly PerfusedTissues
QS·CAQS·CVS
FatQF·CAQF·CVF
ModeratelyPerfused Tissues
QM·CAQM·CVM
DrinkGI Tract
QG·CA
Liver
GSTMFO
QL·CA(QL+QG)·CVLQG·CVG
Com parison of Average Daily Values of Dose M easures and Tum or Incidence in Fem ale M ice after M ethylene Chloride Exposure
Control Inhalation Inhalation Drinking W ater (4000 ppm) (2000 ppm) (250 mg/kg/day)
L iver: C YP450* 0.0 3701 3575 5197 GST 0.0 1810 851 15 Parent 0.0 771 362 6.4 Tum ors (% ) 6 83 33 6
Lung: C YP450 0.0 1583 1531 1227 GST 0.0 256 123 1.0 Parent 0.0 794 381 3.1 Tum ors (% ) 6 85 63 6
* C YP 45 0 and G ST d oses: m g m e tabo lized /lite r t issue /day; P a ren t exposu re : m g /lite r-h r
Tissue Doses for CYP2E21 and GST Pathways of Metabolism H
H Cl
Cl
H
H Cl
Cl
LIVER DOSE LUNG DOSE
Interspecies Dose Comparison for Metabolites from the Glutathione Transferase Pathway
• The solid curve is calculated from the PBPK model for the mouse; the dashed curve is calculated for the human. The straight line is extrapolated based on a linear relationship, as was previously assumed. The difference between the upper and lower lines is about 70 to 80 fold.
Using PBPK Models - 1987Using PBPK Models - 1987
Identify toxic effects in animals and/or people
Evaluate available data on mode(s) of action, metabolism, chemistry of compound, metabolites and related chemicals
Describe potential mode(s) of action
Propose relation between response and tissue dose
Develop a PBPK model to calculate tissue dose(s)
Estimate tissue dose during toxic exposures with model
Estimate risk in humans assuming similar tissue response for equivalent target tissue dose
Rats exposed to 500 ppm CO for 2 hr.
% H
bC
ODevelop PBPK parameters for CO portion of model in absence of DHM exposures.
What about carbon monoxide? Can we develop a PBPK model as well? Sure…
Human volunteers were exposed to 50, 100, 200, and 500 ppm CO (Stewart et al., 1975).
Develop parameters for CO portion of PBPK model for humans.
Human exposure to 50 and 350 ppm dichloromethane: time course of blood carboxyhemoglobin.
Link DHM metabolism to CO production
What can we evaluate with a model of HbCO production from a Dihalomethane?
Metabolism to CO for methylene chloride first noted in a human volunteer study on carbon monoxide.
Volunteer doing paint stripping at home with solvents had high blood HBCO in the morning.
How could this happen?
Blood carboxyhemoglobin levels after half-hour exposures to 5159 ppm dichloromethane or 5000 ppm bromochloromethane (BCM). Triangles are for BCM; circles are for DCM.
Experimental design in rat study !!!What’s going on here? Why do the compounds have different time courses?
N N
NH
CH2CH3
N
CH(CH3)2
H
Cl
N
N N
NH
CH2CH3
N
CH(CH3)2
H
SG
N
N N
NH
CH2CH3
N
H
H
Cl
N
N N
NH
H
N
CH(CH3)2
H
Cl
N
N N
NH
CH2CH3
N
H
H
SG
N
N N
NH
H
N
H
H
Cl
N
N N
NH
H
N
H
H
SG
N
N N
NH
H
N
CH(CH3)2
H
SG
N
GLUTATHIONE CONJUGATES
CONJUGATE / DECHLORINATED METABOLITE ELIMINATION
Krbc CHLORO - TRIAZINES
CYP450 CYP450
CYP450CYP450
GSH
GSH
GSH
I. II.
b) c)
d)
a)Incubations conducted at 4 different atrazine concentrations for 90 min.
All 4 chlorinated triazines were followed in the incubation media.
What do you expect from a study of this kind?
McMullin, T.S. (2005). Integrating tissue dosimetry and mode of action to evaluate atrazine dose response. PhD Thesis, Colorado State University. In press at Toxicology in vitro
Iso Ethyl
DACT
II. Atrazine Metabolism & Inhibition in vitro
Results with atrazine metabolism in rat hepatocytes look quite odd...
What’s going on here? Any Ideas?
1.7
266
44 & 98
Atrazine
Ethyl Isopropyl
DACT
RAMatra = (Vmaxatra*Catra) / (Catra + Katra*(1+Ciso/Kiso + Cethyl/Kethyl + Cdact/Kdact))
RAMatra = (Vmaxatra*Catra) / (Catra + Katra*(1+Ciso/Kiso + Cethyl/Kethyl + Cdact/Kdact))
RAMiso = (Vmaxiso*Ciso) / (Ciso + Kiso*(1+ Cethyl/Kethyl + Catra/KatraCatra/Katra + Cdact/Kdact))
RAMethyl=(Vmaxethyl*Cethyl)/ (Cethyl + KEthyl*(1+Catra/KatraCatra/Katra + Ciso/Kiso + Cdact/Kdact))
Accounting for inhibition of metabolic pathways by multiple substrates
DACT dose-response at 90 minutes comparing model simulations (A) without and (B) with competitive metabolic inhibition terms. Lines represent model simulations.
The non-linear behavior of DACT formation required a model that included competitive inhibition, where high [ATRA] inhibit further metabolism of Iso or Ethyl.
Could it be competitive inhibition???
Hexane (Hx) Exposures & Mixtures
Hx induces changes in mean nerve conduction velocity.
It is more potent at 1000 ppm than at 3000 ppm!
What gives rise to this behavior?
Hexane exposures produce 2,5-HD – the actual neurotoxicant.
Baker and Rikert (1979)
Blood concentrations of 2,5-HD are complexly related to inhaled Hx and have very unintuitive relationships over time.
After cessation of Hx exposure in the 2 higher concentration groups, 2,5-HD actually increases over time.
Where have you seen this behavior?
Hexane PBPK Modeling
Interactions arise from two primary sources:
– competition for a common enzyme required for sequential steps in Hx oxidation
- differential properties of Hx (low blood:air partitioning) versus m-n-BK (much higher blood:air partitioning)
Clewell & Andersen (1984)
OH
O OH
OH
O
O
O
OH
Clearance/Filtration
CYP 2E1
CYP 2E1
Complex dose and time dependencies
HexaneExposure
- Clewell & Andersen (1984)
At higher Hx exposures, 2,5-HD increases after exposure cessation.
Inhibitory interactions present during exposure are released as Hx is rapidly exhaled.
Looks a lot like the atrazine story from the in vitro studies…
Do you believe me? Do you want to buy a bridge?
How could we test if this idea worked with other situations?
Designer Mixture – A lipophilic compound (DBM) metabolized to CO and a poorly soluble anesthetic, isoflurane (ISO), in the air.
What happens to CO?
Develop a PBPK model with inhibition between ISO and DBM. Can you explain why you see the bump?
What do we mean by exposure?
Physiologically Based Pharmacokinetic (PBPK) Modeling
Refine Model Structure
Make Predictions
X
X
X
X
X
XX X
Tis
sue C
on
centr
ati
on
Time
You can be wrong!
Collect NeededData
Metabolic Constants
Tissue Solubility
Tissue Volumes
Blood and Air Flows
Experimental System
Model Equations
Define Realistic Model
Liver
Fat
Body
Lung
Air