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Estimating the Maximum Safe
Starting Dose for First-in-Human
          Clinical Trials

         Beatrice Setnik, Ph.D.
          Research Scientist
          February 12, 2007
Overview
Introduction
Selecting an appropriate dose for First-in-Human
   Trials:
     Determining the No Observed Adverse Effect Level (NOAEL)
     Calculating the Human Equivalent Dose (HED)
     Selecting the most appropriate species
     Applying the Safety Factor
     Considering the Pharmacologically Active Dose (PAD)

Other Considerations
Summary
Safety in Preliminary Clinical Trials
Assessing variability:
   Species-species and species-human differences
      Drug absorption, distribution, metabolism, excretion
      Physiology/ adverse effect profiles
   e.g. Thalidomide
      Teratogenic in humans and not in rats
   e.g. TGN412 (monoclonal antibody)
      March 2006- severe toxicity in six healthy male volunteers in a
       first-in-human clinical trial

Importance of selecting an appropriate and safe
  starting dose
Regulation
FDA Guidance, July 2005
  Guidance for Industry: Estimating the Maximum Safe
    Starting Dose in Initial Clinical Trials for Therapeutics in
    Adult Healthy Volunteers


ICH and Health Canada do not have specific guidance
  document concerning this subject
Objectives
To determine:
   The maximum recommended starting dose (MRSD) for adult
     healthy subjects when beginning a clinical investigation of any
     new drug or biological therapeutic that has been studied in
     animals

Not applicable to:
   Endogenous hormones and proteins (i.e. recombinant clotting
     factors) used at physiological concentrations or prophylactic
     vaccines

Limitations:
   Applies to drug products for which systemic exposure is intended
   Does not address dose escalation or maximum allowable doses in
     clinical trials
Estimating the MRSD
Calculations based on:
   1. Administered doses
   2. Observed toxicities
   3. Algorithmic calculation


Alternatively:
   Animal pharmacokinetic and modeling may be used
   Often insufficient data to construct a scientifically valid PK
      model
Aim of MSRD
Avoid toxicity at initial dose
Dose needs to be high enough to allow reasonably rapid
  attainment of phase I trial objectives (therapeutic
  tolerability, pharmacodynamic (PD) and pharmacokinetic
  (PK) profile)
Data to be Considered
All relevant pre-clinical data
   Pharmacologically active doses
   Full toxicological profile
   PK (absorption, distribution, metabolism and excretion
     [ADME])
The “Algorithm”

 No observed adverse effect
      levels (NOAEL)



  Conversions of NOAEL to
human equivalent dose (HED)




 Determine MRSD based on
           HED
Step 1: NOAEL
No observed adverse effect level (NOAEL) = the
  highest dose level that does not produce a significant
  increase in adverse effects in comparison to the control
  group; where AE are effects that are biological
  significant
NOAEL does not equal NOEL (refers to any effect)
Values identified for each species tested (at least three
  species, one of which in non-rodent)
Step 2: Human Equivalent Dose (HED)

HED is calculated by a conversion based on body surface
  area
Convert all NOAEL to HED
Based on mg/m2 and assumption that there is a 1:1 relation
  between species when body surface area is normalized
Table provided with conversion factor for different species
Step 3: Most Appropriate Species Selection

Selection of the most appropriate HED to use in
  calculation of MRSD
If most appropriate species cannot be determined,
   then most sensitive species should be selected (i.e.
   with the lowest HED)
Most appropriate species based on:
   ADME
   Class experience that indicates a species is more predictive
     of human toxicology
Step 4: Application of Safety Factor
Once HED from NOAEL of the most appropriate (sensitive)
  species is determined a safety factor should be applied
Safety factor applied because
   Variability in extrapolating
   Uncertainty about enhanced sensitivity in humans
   Difficulties in detecting toxicity (e.g. headaches, mental
      disturbances)
   Difference in receptor densities or affinities
   Unexpected toxicities
   Interspecies differences in ADME

Default safety factor is 10X
   Increased/decreased under certain circumstances
Step 4: Application of Safety Factor
Increasing the Safety Factor (> 10)
   Steep dose response curve
   Severe toxicities
   Nonmonitorable toxicity
   Toxicities without premonitory signs
   Variable bioavailability
   Irreversible toxicity
   Unexplained mortality
   Large variability in doses of plasma drug levels eliciting effects
   Nonlinear pharmacokinetics
   Inadequate dose-response data
   Novel therapeutic targets
   Animal models with limited utility
Step 4: Application of Safety Factor
Decreasing the Safety Factor (< 10)
  Usually for therapeutics of a well characterized class
      Administered by same route schedule and duration
      Similar metabolic profile and bioavailability
      Similar toxicity profiles across all the species tested including humans

  Toxicity is easily monitored, reversible, predictable and exhibits a
    moderate-to-shallow dose-response relationship with toxicities
    consistent across tested species

  NOAEL determined based on toxicity studies of a longer duration
    compared to the proposed clinical schedule in healthy volunteers
      Assumes that toxicities are cumulative, are not associated with acute
        peaks in therapeutic concentrations and did not occur early in the
        repeated dose study
Step 5: Consideration of the
         Pharmacologically Active Dose
Pharmacologically Active Dose (PAD)
MRSD compared to PAD
PAD estimation not described in guidance, but should
  be considered in determining the initial starting
  dose in humans.
PAD may be lower than the MRSD and there may be
  cases where this dose is used instead of the
  calculated MRSD.
Additional Considerations

FDA has started an initiative to allow first in man
  studies using microdoses
   Less than 1/100th of the dose calculated to yield a pharmacological
     effect
   Concerns with high potency agents
Additional Considerations
Expert Scientific Group on Phase One Clinical Trials; UK,
  30th Nov. 2006
   In general, the more species-specific an agent is, the less reliable will be the
       information from animal studies as a guide to selecting the starting dose in
       humans
   If different methods give different estimates of the MRSD, the lowest value
       should be used
   Minimum Anticipated Biological Effect Level (MABEL) recommended as a
       useful approach to calculate safe starting dose
       More conservative estimate
Summary
Dose selection
  Key objective is safety
  Conservative approach
  5 steps to calculate MRSD
  Other strategies (e.g. microdose, MABEL)


FDA guidelines
  Limited to drugs, clinical trials involving health human
    volunteers
Thank You.

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Estimating the Maximum Safe Starting Dose for First-in-Human Clinical Trials

  • 1. Estimating the Maximum Safe Starting Dose for First-in-Human Clinical Trials Beatrice Setnik, Ph.D. Research Scientist February 12, 2007
  • 2. Overview Introduction Selecting an appropriate dose for First-in-Human Trials: Determining the No Observed Adverse Effect Level (NOAEL) Calculating the Human Equivalent Dose (HED) Selecting the most appropriate species Applying the Safety Factor Considering the Pharmacologically Active Dose (PAD) Other Considerations Summary
  • 3. Safety in Preliminary Clinical Trials Assessing variability: Species-species and species-human differences Drug absorption, distribution, metabolism, excretion Physiology/ adverse effect profiles e.g. Thalidomide Teratogenic in humans and not in rats e.g. TGN412 (monoclonal antibody) March 2006- severe toxicity in six healthy male volunteers in a first-in-human clinical trial Importance of selecting an appropriate and safe starting dose
  • 4. Regulation FDA Guidance, July 2005 Guidance for Industry: Estimating the Maximum Safe Starting Dose in Initial Clinical Trials for Therapeutics in Adult Healthy Volunteers ICH and Health Canada do not have specific guidance document concerning this subject
  • 5. Objectives To determine: The maximum recommended starting dose (MRSD) for adult healthy subjects when beginning a clinical investigation of any new drug or biological therapeutic that has been studied in animals Not applicable to: Endogenous hormones and proteins (i.e. recombinant clotting factors) used at physiological concentrations or prophylactic vaccines Limitations: Applies to drug products for which systemic exposure is intended Does not address dose escalation or maximum allowable doses in clinical trials
  • 6. Estimating the MRSD Calculations based on: 1. Administered doses 2. Observed toxicities 3. Algorithmic calculation Alternatively: Animal pharmacokinetic and modeling may be used Often insufficient data to construct a scientifically valid PK model
  • 7. Aim of MSRD Avoid toxicity at initial dose Dose needs to be high enough to allow reasonably rapid attainment of phase I trial objectives (therapeutic tolerability, pharmacodynamic (PD) and pharmacokinetic (PK) profile)
  • 8. Data to be Considered All relevant pre-clinical data Pharmacologically active doses Full toxicological profile PK (absorption, distribution, metabolism and excretion [ADME])
  • 9. The “Algorithm” No observed adverse effect levels (NOAEL) Conversions of NOAEL to human equivalent dose (HED) Determine MRSD based on HED
  • 10. Step 1: NOAEL No observed adverse effect level (NOAEL) = the highest dose level that does not produce a significant increase in adverse effects in comparison to the control group; where AE are effects that are biological significant NOAEL does not equal NOEL (refers to any effect) Values identified for each species tested (at least three species, one of which in non-rodent)
  • 11. Step 2: Human Equivalent Dose (HED) HED is calculated by a conversion based on body surface area Convert all NOAEL to HED Based on mg/m2 and assumption that there is a 1:1 relation between species when body surface area is normalized Table provided with conversion factor for different species
  • 12.
  • 13. Step 3: Most Appropriate Species Selection Selection of the most appropriate HED to use in calculation of MRSD If most appropriate species cannot be determined, then most sensitive species should be selected (i.e. with the lowest HED) Most appropriate species based on: ADME Class experience that indicates a species is more predictive of human toxicology
  • 14. Step 4: Application of Safety Factor Once HED from NOAEL of the most appropriate (sensitive) species is determined a safety factor should be applied Safety factor applied because Variability in extrapolating Uncertainty about enhanced sensitivity in humans Difficulties in detecting toxicity (e.g. headaches, mental disturbances) Difference in receptor densities or affinities Unexpected toxicities Interspecies differences in ADME Default safety factor is 10X Increased/decreased under certain circumstances
  • 15. Step 4: Application of Safety Factor Increasing the Safety Factor (> 10) Steep dose response curve Severe toxicities Nonmonitorable toxicity Toxicities without premonitory signs Variable bioavailability Irreversible toxicity Unexplained mortality Large variability in doses of plasma drug levels eliciting effects Nonlinear pharmacokinetics Inadequate dose-response data Novel therapeutic targets Animal models with limited utility
  • 16. Step 4: Application of Safety Factor Decreasing the Safety Factor (< 10) Usually for therapeutics of a well characterized class Administered by same route schedule and duration Similar metabolic profile and bioavailability Similar toxicity profiles across all the species tested including humans Toxicity is easily monitored, reversible, predictable and exhibits a moderate-to-shallow dose-response relationship with toxicities consistent across tested species NOAEL determined based on toxicity studies of a longer duration compared to the proposed clinical schedule in healthy volunteers Assumes that toxicities are cumulative, are not associated with acute peaks in therapeutic concentrations and did not occur early in the repeated dose study
  • 17. Step 5: Consideration of the Pharmacologically Active Dose Pharmacologically Active Dose (PAD) MRSD compared to PAD PAD estimation not described in guidance, but should be considered in determining the initial starting dose in humans. PAD may be lower than the MRSD and there may be cases where this dose is used instead of the calculated MRSD.
  • 18. Additional Considerations FDA has started an initiative to allow first in man studies using microdoses Less than 1/100th of the dose calculated to yield a pharmacological effect Concerns with high potency agents
  • 19. Additional Considerations Expert Scientific Group on Phase One Clinical Trials; UK, 30th Nov. 2006 In general, the more species-specific an agent is, the less reliable will be the information from animal studies as a guide to selecting the starting dose in humans If different methods give different estimates of the MRSD, the lowest value should be used Minimum Anticipated Biological Effect Level (MABEL) recommended as a useful approach to calculate safe starting dose More conservative estimate
  • 20. Summary Dose selection Key objective is safety Conservative approach 5 steps to calculate MRSD Other strategies (e.g. microdose, MABEL) FDA guidelines Limited to drugs, clinical trials involving health human volunteers