1 april 6 – 7, 2010 us epa exposure-based chemical prioritization workshop: exploring...

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1 April 6 – 7, 2010 US EPA Exposure-Based Chemical Prioritization Workshop: Exploring Opportunities for Collaboration Rapid Estimates of ADME Rapid Estimates of ADME Daniel T. Chang a , Michael-Rock Goldsmith a , Thomas R. Transue c , Rogelio Tornero-Velez a , Shane D. Peterson b , Yu-Mei Tan and Curtis C. Dary b a National Exposure Research Laboratory, US Environmental Protection Agency, Research Triangle Park, NC 27711, USA b National Exposure Research Laboratory, US Environmental Protection Agency, Las Vegas, NV 89119, USA c Lockheed-Martin Information Technology, Research Triangle Park NC, USA Disclaimer: This presentation does not necessarily reflect EPA policy. Mention of trade names or commercial products does not constitute endorsement or recommendation for use.

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Page 1: 1 April 6 – 7, 2010 US EPA Exposure-Based Chemical Prioritization Workshop: Exploring Opportunities for Collaboration Rapid Estimates of ADME Daniel T

1April 6 – 7, 2010

US EPA Exposure-Based Chemical Prioritization Workshop: Exploring Opportunities for Collaboration

Rapid Estimates of ADMERapid Estimates of ADME

Daniel T. Changa, Michael-Rock Goldsmitha, Thomas R. Transuec,Rogelio Tornero-Veleza, Shane D. Petersonb, Yu-Mei Tan and Curtis C. Daryb

aNational Exposure Research Laboratory, US Environmental Protection Agency, Research Triangle Park, NC 27711, USAbNational Exposure Research Laboratory, US Environmental Protection Agency, Las Vegas, NV 89119, USA

cLockheed-Martin Information Technology, Research Triangle Park NC, USA

Disclaimer: This presentation does not necessarily reflect EPA policy. Mention of trade names or commercial products does not constitute endorsement or recommendation

for use.

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Outline• Background– Model needs– Estimation methods– PReParE

• A case study: ADME Scoping the PBPK Chemical Landscape

• Summary

Page 3: 1 April 6 – 7, 2010 US EPA Exposure-Based Chemical Prioritization Workshop: Exploring Opportunities for Collaboration Rapid Estimates of ADME Daniel T

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Extrapolations in Chemical Risk Assessments

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Exposure to Dose Extrapolation

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Extrapolating from Exposure to Dose:model needs

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Generalized In Silico Profiling Workflow

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Computational Molecular Modeling for Evaluating the Toxicity of Environmental Chemicals: Prioritizing Bioassay Requirements

James R. Rabinowitz, Michael-Rock Goldsmith, Stephen B. Little, and Melissa A. Pasquinelli

Environ Health Perspect. 2008 May; 116(5): 573–577. Published online 2008 February 1. doi: 10.1289/ehp.11077.

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Physiologically Relevant Parameter Estimation(PReParE)

Page 8: 1 April 6 – 7, 2010 US EPA Exposure-Based Chemical Prioritization Workshop: Exploring Opportunities for Collaboration Rapid Estimates of ADME Daniel T

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Chemical Input, Simple to Complex SAR

Upper: screen capture of main input screen. For chemical specific parameters to be calculated the option to select (cyan) MOE-WEB to draw an individual structure and obtain relevant descriptors to be used subsequently in all RED input areas. A list of some simple QSAR established from the literature can be found here by mousing over the data predicted or the description of the individual QSAR. This will be continuously augmented with additional QSAR, such as those arising from QikProp (Schrodinger Inc.)

Middle: screen capture of PROPHET (Probabilistically Plausible Heuristic Enrichment of Targets) a knowledge base of > 7500 chemical/biomolecular target affinity values was mined for statistical data for 6 key descriptors (LogP, TPSA: topological polar surface area, rotatble bond count, number of H-bond donors and acceptors and molecular weight). The more likely a chemical is to be attributed to a target for which multiple of the discrete descriptors fall within the statistically sampled distribution for a given target. All filters derived from culling the KiBank dataset.

Page 9: 1 April 6 – 7, 2010 US EPA Exposure-Based Chemical Prioritization Workshop: Exploring Opportunities for Collaboration Rapid Estimates of ADME Daniel T

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Mechanistic Tissue:Plasma Calculator

rat and human (Poulin & Thiel, 2002)

Page 10: 1 April 6 – 7, 2010 US EPA Exposure-Based Chemical Prioritization Workshop: Exploring Opportunities for Collaboration Rapid Estimates of ADME Daniel T

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Physiological Parameter Calculators

tissue-specific mRNA expression profiles for HUMAN Phase I and II metabolism enzymes and nuclear receptors

human, mouse, rat and dog:total weight, % total weight of tissue, % cardiac output of tissue

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PAVA rendering of oral route ethanol PAVA rendering of oral route ethanol (fasting) PBPK model output(fasting) PBPK model output

1: Levitt DG. PKQuest: measurement of intestinal absorption and first pass1: Levitt DG. PKQuest: measurement of intestinal absorption and first passmetabolism - application to human ethanol pharmacokinetics. BMC Clin Pharmacol.metabolism - application to human ethanol pharmacokinetics. BMC Clin Pharmacol.2002 Aug 15;2:4. PubMed PMID: 12182761; PubMed Central PMCID: PMC122094.2002 Aug 15;2:4. PubMed PMID: 12182761; PubMed Central PMCID: PMC122094.

NOTE:NOTE: Multi-compartment PBPK schema above for illustrative purposes only Multi-compartment PBPK schema above for illustrative purposes onlyGraphic from: Graphic from: http://commons.wikimedia.org/wiki/File:7-cpt_PBPK_model.png““Symbolic representation of a 7-compartment PBPK model” – Frederic Y BoisSymbolic representation of a 7-compartment PBPK model” – Frederic Y Bois

PAVA:Physiological and Anatomical Visual Analytics

Rendering of anatomically-relevant data onto human organs (PK, gene expression, epidemiology etc…)

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Case Study: ADME Scoping the PBPK Chemical Landscape (NHANES, ToxCastTM and USDA-PDP)

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• Can we draw molecular-derived relationships among a disparate set of chemicals?

• Can we compare among different classes and/or databases?

• What are the key molecular features that describe each set?

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Simple ADME Space Scoping

mol MW SASA volume QPPCaco QPlogBB QPPMDCK QPlogKp QPlogKhsa PSATOXCAST avg 304.90 539.57 925.63 2456.40 -0.30 3917.87 -2.22 -0.06 65.92

std 97.37 123.58 258.75 2373.97 0.61 3640.73 1.21 0.55 34.83USDA avg 247.74 533.49 908.23 2837.05 -0.37 2929.60 -2.09 -0.14 61.84

std 72.75 99.83 199.35 2702.90 0.48 3074.62 1.23 0.62 28.91NHANES avg 243.49 428.09 707.76 2933.65 -0.30 2987.43 -2.24 -0.22 53.31

std 121.95 118.23 235.96 3506.23 0.62 3622.80 1.11 0.51 41.61PBPK avg 159.20 328.91 506.83 7136.33 0.08 6083.41 -1.87 -0.33 18.52

std 125.70 125.07 250.47 3707.37 0.76 3798.50 1.44 0.60 35.33ALL avg 277.31 506.52 858.87 3027.93 -0.29 3723.86 -2.16 -0.12 59.17

std 105.73 133.62 271.86 3031.92 0.60 3600.73 1.23 0.58 36.60

• Generalized observed trends in evaluated ADME related properties:

– PBPK chemicals (on average) are smaller in molecular weight (almost half) than the 3 compared databases

– TOXCASTTM chemicals tend to be larger in molecular weight

– Evaluated properties are consistent with the simple MW analysis.

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Chemical Space Analysis (PCA)using ChemGPS-NP

“The first four dimensions of the ChemGPS-NP map, accounting for 77% of data variance…Any compound with a known chemical structure can be positioned onto this map using interpolation interms of PCA score prediction. From the resulting

projections properties of the compounds can be compared and easily interpreted together with trends and clusters”

– ChemGPS-NP, Larsson, 2009

pc1

pc1,pc2,pc3 pc1,pc2,pc4

pc2

pc3/pc4

“pbpk space”Nhanes biomarkersUSDA-PDPToxCast 320

– Principal component 1 (pc1): size, shape and polarizability

– Principal component 2 (pc2): aromatic and conjugation related properties

– Principal component 3 (pc3): lipophilicity, polarity, and H-bond capacity

– Principal component 4 (pc4): molecular flexibility and rigidity

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PBPK Model “Inspired” Hyper-Surface

5

4

3

2

1

0

-1

-2

-10 -5 -4 -3 -2 -1 1 2 3

PBPK spaceNhanes biomarkersUSDA-PDPToxCast 320Obach

Log Ka/w

Lo

g K

o/w

breath

urinary

fecal~70% overlap between USDA-PDP and ToxCastTM 320

~40% overlap between NHANES and ToxCastTM 320

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Fu

Thalf (hr)

NRs

cyp450

logMW x 10

Lo

gP

(o/w

)

Metabolic Trends From the Obach 670 Dataset

Obach RS, Lombardo F, Waters NJ. Trend analysis of a database of intravenous pharmacokinetic parameters in humans for 670 drug compounds. Drug Metab Dispos. 2008 Jul;36(7):1385-405. Epub 2008 Apr 21

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The Future….

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Summary

• Exposure is highly dependent on chemistry and biology and understanding ADME is key to elucidating the links (cusps) between exposure and internal doses that lead to health outcomes.

• Use of pharmacokinetic models requires detailed information on ADME. In the absence of such information, we need to evaluate parameters rapidly either as surrogates or initial starting parameters (e.g., Bayesian).

• ADME and chemical space scoping is highly dependent on knowledge mining capabilities, but simplifies analysis of large datasets (i.e., gives us the big picture on hundreds to thousands of chemicals)

• Allows us to group chemicals based on molecular space:– Leads to better understanding of the chemicals within large

datasets: Where do we need to concentrate our efforts? Where are the data gaps?, What should we be concerned with?, etc.

– Rapid assessment dependent on available chemical structures (Caution must be used for chiral compounds and mixtures esp. with respect to metabolism)

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Appendix: extra slides and links

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Real-time in vivo pharmacokinetics?Whole-Body Autoradiography

Yaghoubi, S.S. et al. Human pharmacokinetic and dosimetry studies of [18F]FHBG: a reporter probe for imaging herpes simplex virus type-1 thymidine kinase reporter gene expression. J. Nucl. Med. 42, 1225–1234 (2001).

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Beer and burgers

Where does all that alcohol go?

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Comparative Pharmacokinetics: Fatty Diet – Fasting Diet

Differential kinetics as a function of food intake

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