AGRICULTURAL CHEMICAL SAFETY ASSESSMENT (ACSA)

Similar documents
FDA Expectations and Evaluation of Inhalation Toxicology Studies

Dermal Occupational Exposure Limits. Their use in risk assessment

Cycloxydim CYCLOXYDIM (179)

SCIENTIFIC COMMITTEE ON TOXICITY, ECOTOXICITY AND THE ENVIRONMENT (CSTEE) Opinion on the results of the Risk Assessment of:

Pharmacokinetic and absolute bioavailability studies in early clinical development using microdose and microtracer approaches.

EVALUATION OF POLYCYCLIC AROMATIC HYDROCARBONS IN CLAY TARGET FRAGMENTS AND SURFACE SOIL AT SHOT GUN RANGE SITES Presenter: Glenn Hoeger and Brian

METHODOLOGIES FOR INTERMITTENT AND SHORT-TERM EXPOSURE TO CARCINOGENS SUBCOMMITTEE

Introduction to. Pharmacokinetics. University of Hawai i Hilo Pre-Nursing Program NURS 203 General Pharmacology Danita Narciso Pharm D

TNsG on Annex I Inclusion Revision of Chapter 4.1: Quantitative Human Health Risk Characterisation

Case Study Application of the WHO Framework for Combined Exposures. Presented by: M.E. (Bette) Meek University of Ottawa

Nonclinical Safety Evaluation of Inhalation Drug Products

APPLICATION FOR AUTHORISATION: ESTABLISHING REFERENCE DNELS FOR BBP

Pesticide Product Labels What the label says.and Why. Dr. Jeff Birk BASF Corporation Regulatory Manager

APPLICATION FOR AUTHORISATION: ESTABLISHING REFERENCE DNELs FOR 1-BROMOPROPANE (1-BP)

Absolute bioavailability and pharmacokinetic studies in early clinical development using microdose and microtracer approaches.

Early Life Development of Toxicokinetic Pathways: Framework Case Examples and Implications for Safety Assessment

A Weight of Evidence Approach to Cancer Assessment. Alan R Boobis Imperial College London

Principles of Toxicokinetics/Toxicodynanics

EFSA GD on dermal absorption Industry feedback and considerations on bridging opportunities

1. If the MTC is 100 ng/ml and the MEC is 0.12 ng/ml, which of the following dosing regimen(s) are in the therapeutic window?

Bayer Environmental Science

Overview of US EPA Assessment Activities for Perfluorooctanoic Acid (PFOA) and Perfluorooctane Sulfonate (PFOS)

Considerations in Toxicology Study Design and Interpretation: An Overview Gradient Corporation: Lewis, AS; Beyer, LA; Langlois, CJ; Yu, CJ; Wait, AD

Ensuring Safety for Early Life Exposures: Adequacy of Current Methods and Opportunities to Advance the Science

Dose response relationships: biological and modeling aspects

Risk Assessment of Chemicals in Foods- WHO Principles and Methods

Criteria for toxicological characterization metabolites and testing strategy

5.36 THIOPHANATE-METHYL (077)

Committee for Risk Assessment (RAC)

The Director General Maisons-Alfort, 30 July 2018 OPINION. of the French Agency for Food, Environmental and Occupational Health & Safety

Bayer Environmental Science

DMPK. APRIL 27 TH 2017 Jan Neelissen Scientific Adviser Science & Technology

Basic Concepts of TDM

CANCER HAZARD IDENTIFICATION STRATEGIES PROJECT COMMITTEE

STUDIES TO EVALUATE THE SAFETY OF RESIDUES OF VETERINARY DRUGS IN HUMAN FOOD: GENERAL APPROACH TO ESTABLISH AN ACUTE REFERENCE DOSE

Robert G. Sussman, Ph.D., DABT Managing Principal, Eastern Operations. SafeBridge Consultants, Inc. Mountain View, CA New York, NY Liverpool, UK

CLINICAL PHARMACOKINETICS INDEPENDENT LEARNING MODULE

Protein Safety Assessments Toxicity and Allergenicity

Basic Biopharmaceutics, Pharmacokinetics, and Pharmacodynamics

Preclinical Requirements for Therapeutic Studies in Humans with Advanced Cancer

N-Methylneodecanamide (MNDA)

Basic toxicology and biomaterials testing

Conflict of Interest Statement

Exposure Dose Health Effects

5.3 AZINPHOS METHYL (002)

Tracer studies in GSK for Discovery and Development

5.15 HEXYTHIAZOX (176)

The Importance of ADME/PK to Inform Human Safety Assessments Based on Animal Studies: Example with Furan. Gregory L. Kedderis, PhD Chapel Hill, NC

Strategies for health interpretation: development of HBM healthbased guidance values for individual phthalates and BPA

BIOPHARMACEUTICS and CLINICAL PHARMACY

BASIC PHARMACOKINETICS

Laszlo Tothfalusi Ph.D. Dept. Phrmacodynamics Semmelweis University, Budapest

HEALTH CONSULTATION. Tom Lea Park EL PASO COUNTY METAL SURVEY EL PASO, EL PASO COUNTY, TEXAS EPA FACILITY ID: TX

Principles of Toxicology The Study of Poisons

Click to edit Master title style

Bayer Environmental Science

alternative short-chain fluorinated product technology

Read Across with Metabolomics for Phenoxy Herbicides a Case Study with MCPP BASF SE

COMMITTEE FOR VETERINARY MEDICINAL PRODUCTS

1 Introduction: The Why and How of Drug Bioavailability Research

Glyphosate Hazard and Risk Assessment: A Comparison of the Approaches of Two International Agencies

Bayer Environmental Science

PHA Final Exam. Fall On my honor, I have neither given nor received unauthorized aid in doing this assignment.

Risk Assessment Report on Tris (nonylphenyl)phosphite (TNPP)

Section 5.2: Pharmacokinetic properties

Risk Characterization

Bayer Environmental Science

Distinguishing between Mode and Mechanism of Action

Regulatory Toxicology and Pharmacology

Mitigation of risk and selection of clinical starting dose a PMDA nonclinical perspective

OECD GUIDELINE FOR THE TESTING OF CHEMICALS

Guidance Document for the Use of Data in Development of Chemical-Specific Adjustment Factors (CSAFs) for Interspecies Differences and Human

Chemical Name: Metolachlor OXA CAS: Synonyms: Oxanilic acid degradate of metolachlor

General Principles of Pharmacology and Toxicology

Human ADME Study Design Considerations in Healthy Subjects and in Patients

Thought Starter Combined Exposures to Multiple Chemicals Second International Conference on Risk Assessment

Pharmacokinetics of strong opioids. Susan Addie Specialist palliative care pharmacist

Science Policy Notice

LD = (Vd x Cp)/F (Vd x Cp)/F MD = (Css x CL x T)/F DR = (Css x (Vm-DR))/Km Css = (F x D)/(CL x T) (Km x DR)/(Vm DR)

Risk assessment of organic verses inorganic arsenic; The toxicity of arsenite and arsenate; and Ongoing bioavailability study.

Tissue Dose Based Risk Assessments

Bayer Environmental Science

Take-Home Exam Distributed: October 19, 2012, at 2:30 p.m. Due: October 24, 2012, at 1:30 p.m.

Predicting Maternal Rat and Pup Exposures: How Different are They?

PHA 5127 FINAL EXAM FALL On my honor, I have neither given nor received unauthorized aid in doing this assignment.

OpenFoodTox and Other Open Source In silico EFSA. Jean Lou Dorne Senior Scientific Officer Scientific Committee and Emerging Risks Unit EFSA

PHA Second Exam. Fall On my honor, I have neither given nor received unauthorized aid in doing this assignment.

TRIS (NONYLPHENYL) PHOSPHITE SUMMARY RISK ASSESSMENT REPORT

Bayer Environmental Science

Application of the WHO Framework for Combined Exposures; Implications for Combined Exposures Assessment

Dithianon DITHIANON (180)

Incorporating Gene-Environment Information into Kinetic Models: Lessons Learned and Future Challenges

Using Accelerator Mass Spectrometry to Explain the Pharmacokinetics of Vismodegib Cornelis E.C.A. Hop

Challenges in Nonclinical Development of Inhalation Drug Products

Renal Impairment From Dettli to Guideline: What can we learn?

NOTE FOR GUIDANCE ON TOXICOKINETICS: THE ASSESSMENT OF SYSTEMIC EXPOSURE IN TOXICITY STUDIES S3A

Absorption, Distribution, Metabolism, Excretion and Toxicology

DANIEL R. DOERGE U.S. Food and Drug Administration National Center for Toxicological Research Jefferson, AR

European public MRL assessment report (EPMAR)

Principles of Toxicology: The Study of Poisons

Transcription:

HESI ILSI Health and Environmental Sciences Institute AGRICULTURAL CHEMICAL SAFETY ASSESSMENT (ACSA) ADME Task Force Hugh A. Barton, PhD National Center for Computational Toxicology Office of Research and Development US Environmental Protection Agency Research Triangle Park, NC November 16, 2005

Hazard Characterization and Dose-Response Framework Response Response Toxicity Pathway Mode of Action Tissue Dosimetry Toxicodynamics Pharmacokinetics/ Toxicokinetics limited information default Exposure Exposure Qualitative Organization and Analysis Quantitative Analysis

Dose-Response-Time High Dose Mid Low Animal Testing Human Exposure Time

Purpose of ADME Studies Dose-Response: Obtain information to help determine the relationship between the concentration of free compound in plasma and the toxicological response. Risk: Provide data that assists in the design and interpretation of toxicity studies and the determination of risk.

Objectives Develop guidance for the careful, tierwise collection of PK data that would better define dose across species life stages route frequency and duration of exposure

Objectives (continued) Provide recommendations that would help in Toxicology study design Interpretation Risk Assessment

Working through the process Route-Route Animal to Human Worker Safety Risk? Tox Studies Basic Tier I ADME -Time Course -Metabolites -Bioavailability -Saturation -Recovery Advanced Tier III Interpret Custom Tier II -Route -Age -Species Internal Dose Species Differences Mode of Action

Basic Tier I Oral Bioavailability (iv, oral) Metabolism and Elimination Dose-Dependent PK Repeated-Exposure PK Blood levels in toxicity studies

Assisting in Dose Selection Dose selection for chronic studies would be improved with a bioavailability assessment. This is an example of saturation of oral absorption at doses >7000 ppm in diet: μg/ml plasma 80 70 60 50 Plasma Time-Course: Dietary Exposure 40 30 20 10 0 1h 2h 3h 4h 5h 6h 7h Time 1000 ppm 7000 ppm 50 000 ppm

Working through the process Route-Route Animal to Human Worker Safety Risk? Tox Studies Basic Tier I ADME -Time Course -Metabolites -Bioavailability -Saturation -Recovery Advanced Tier III Interpret Custom Tier II -Route -Age -Species Internal Dose Species Differences Mode of Action

For Interpretation Dose-Response Mode of Action Internal Dose

Custom Tier II Studies Non-rodent PK Tissue/fluid distribution (including fetus/milk) In vitro metabolism: rodents/humans Serum protein binding Biliary excretion/enterohepatic recirculation

Example: Species Relevance The dog is uniquely more sensitive to organic acids like 2,4-D. Renal clearance studies suggest that the dog has a low capacity to excrete organic acids. Allometric comparison of the pharmacokinetic parameters: volume distribution (Vd), renal clearance (Cl) and plasma half-life (t 1/2 ) were conducted across species (including human). Conclusion: the dog is an outlier.

100 A. 100000 B. Vd L 10 1 0.1 Pig Dog Calf Human Cl ml hr-1 10000 1000 100 Rat Pig Calf Human Human 0.01 Mice Rat 10 1 Mice Dog 0.001 0.01 0.1 1 10 100 Comparative Species PK Body Weight (kg) t1/2 hr 1000 100 10 C. 0.1 0.01 0.1 1 10 100 Body Weight (kg) 5 mg/kg Dog 1 mg/kg Human Pig Calf 1 Mice Rat 0.1 0.01 0.1 1 10 100 Body Weight (kg)

Working through the process Route-Route Animal to Human Worker Safety Risk? Tox Studies Basic Tier I ADME -Time Course -Metabolites -Bioavailability -Saturation -Recovery Advanced Tier III Interpret Custom Tier II -Route -Age -Species Internal Dose Species Differences Mode of Action

Advanced Tier III Route-to-Route Extrapolation Dermal»In vitro rat/human»in vivo rat Inhalation Biomonitoring Human clinical PK

Working through the process New Compound: Route-Route Animal to Human Worker Safety Risk? Tox Studies Basic Tier I ADME -Time Course -Metabolites -Bioavailability -Saturation -Recovery Advanced Tier III Interpret Custom Tier II -Route -Age -Species Internal Dose Species Differences Mode of Action

Working through the process Mature Compound: Route-Route Animal to Human Worker Safety Risk? Tox Studies Basic Tier I ADME -Time Course -Metabolites -Bioavailability -Saturation -Recovery Advanced Tier III Interpret Custom Tier II -Route -Age -Species Internal Dose Species Differences Mode of Action

Example Tier III Study: Human dermal absorption Dermal is a major exposure route. In vitro studies can provide an initial estimate of dermal absorption. In vivo studies with human volunteers can establish extent of dermal absorption. Direct application for assessing human health risk.

Conclusions/Recommendations To be useful, ADME studies need to: Help in the design of toxicity studies. Help interpret results from toxicity studies. Help assess risk.

Conclusions/Recommendations (continued) Generalized tiered approach Basic (Tier I), which would include data that are crucial for toxicity study design including dose selection, half-life determinations for recovery period determination, and the identification of major metabolites. Custom (Tier II), which would include data needed for study interpretation, absorbed dose estimates, and duration/route extrapolations. Advanced (Tier III), which would include data to support the understanding of a compound s mode of action and allow the derivation of pharmacodynamic concordance.

ADME Task Force Members Co-Chairs: Hugh Barton (USEPA) and Timothy Pastoor (Syngenta Crop Protection) Karl Baetcke (US EPA) Jan Chambers (MS State University) Janet Diliberto (US EPA) Jeff Driver (infoscientific.com) Chuck Hastings (BASF) Sesh Iyengar (Bayer CropScience) Robert Krieger (University of CA, Riverside) Bernhard Stahl (Bayer CropScience) Chuck Timchalk (Pacific NW National Laboratory) LIAISONS: Alan Boobis (Imperial College London) Systemic Toxicity Task Force Larry Sheets (Bayer Corporation) Life Stages Task Force