Sensitivity study of dose-finding methods

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Transcription:

to of dose-finding methods Sarah Zohar 1 John O Quigley 2 1. Inserm, UMRS 717,Biostatistic Department, Hôpital Saint-Louis, Paris, France 2. Inserm, Université Paris VI, Paris, France. NY 2009 1 / 21

to in trial allocation and final recommendation 1 To the Undetected toxicities Incorrectly recorded toxicities as dose limiting toxicities 2 To the choice of arbitrary parameters of the design Dose-toxicity NY 2009 2 / 21

1. to (1) to Probability of toxicity R i = Pr (Y j = 1 X j = d i ) To this we define a new variable, V j, which corresponds to the true toxicity for patient j. Y j our observation which we would hope to be as often as possible the same as V j. NY 2009 3 / 21

1. to (2) to λ 1 corresponds to the probability of incorrectly missing a toxicity and classifying it as a non-toxicity Pr(Y j = 1 V j = 1) = 1 λ 1 λ 2 corresponds to the probability classifying a non-toxicity as a toxicity. Pr (Y j = 0 V j = 0) = 1 λ 2 The probability of observing a toxicity is given by: Pr(Y j = 1) = (1 λ 1 )Pr(V j = 1) + λ 2 Pr(V j = 0) The probability of not observing a toxicity is given by: Pr(Y j = 0) = λ 1 Pr(V j = 1) + (1 λ 2 )Pr(V j = 0) NY 2009 4 / 21

Simulations (1) Simulations over 200 dose-toxicity relationships to NY 2009 5 / 21

Simulations (2) to N=36 Toxicity target=0.3 6 dose levels 1000 independent replications of each scenario Three dose-finding designs: 3+3 group up-and-down design (UD(s, c L, c U )) with UD s = 2, c L = 0 and c U = 1 LCRM with α 1 = 0.1, α 2 = 0.3, α 3 = 0.5, α 4 = 0.6, α 5 = 0.7 and α 6 = 0.8 NY 2009 6 / 21

Simulations (3) λ 1 : The probability of incorrectly missing a toxicity and classifying it as a non-toxicity to Cumulative distribution of errors where the error itself is defined to be the arithmetic distance between the probability of toxicity at the level recommended and the probability of toxicity at the MTD NY 2009 7 / 21

Simulations (4) λ 2 : The probability of classifying a non-toxicity as a toxicity to NY 2009 8 / 21

Conclusions (1) to The error associated with incorrectly recorded toxicities has a higher influence on the trial final recommendation than the error associated with undetected toxicities. The first type of error is where we record an actual toxicity as a non-toxicity and the impact of this is more complex. As far as recommendation of the MTD is concerned then our results show that, as long as the rate of errors of the first type is not too high, the overall design is robust to this. At the same time, from a clinical viewpoint, those patients treated in the dose-finding itself have a greater risk of being exposed to doses which are higher than otherwise they would have been. NY 2009 9 / 21

2. dose-toxicity to Would we have recommended the same MTD if we had worked with a CRM design specified differently? Retrospective analysis Special considerations needed to analyze sequential data retrospectively. Observations need to be correctly weighted. Weights are calculated at each dose based on observed data and response at each dose level. Weights are used to obtain an estimate of model parameters. Estimated model parameters provide an estimate of the MTD *O Quigley J.,Biometrics 2005; 61: 749 56 NY 2009 10 / 21

dose-toxicity to Retrospective analysis Weights w j (d i ) are calculated for all available doses W j (a) = k w j (d i )U ij (a) with U ij (a) the log-likelihood function that can be rewritten as: U j (a) = 1 j j ψ {y l l=1 i=1 ψ (x l, a) + (1 y l ) ψ 1 ψ (x l, a) } The solution to the equation W n(a) is obtained when: k i=1 ψ w n(d i ) [R ] i ψ (x i, a) + (1 R i ) ψ 1 ψ (x i, a) = 0 The weighted are used to obtain an estimate of the model parameter a NY 2009 11 / 21

Simulations (1) Working Model d 1 d 2 d 3 d 4 d 5 d 6 WM 1 0.20 0.30 0.45 0.60 0.70 0.80 WM 2 0.05 0.10 0.30 0.50 0.60 0.65 WM 3 0.01 0.02 0.09 0.30 0.40 0.45 WM 4 0.00 0.00 0.02 0.07 0.30 0.41 WM 5 0.01 0.02 0.05 0.07 0.10 0.30 WM 6 0.01 0.10 0.30 0.45 0.65 0.85 to Probability 0.0 0.2 0.4 0.6 0.8 1.0 Working Model 1 WM 2 WM 3 WM 4 WM 5 WM 6 Toxicity target 1 2 3 4 5 6 NY 2009 12 / 21

Simulations (2) Working Model d 1 d 2 d 3 d 4 d 5 d 6 WM 7 0.35 0.50 0.55 0.60 0.65 0.70 WM 8 0.01 0.03 0.07 0.10 0.15 0.22 WM 9 0.10 0.20 0.30 0.40 0.50 0.60 WM 10 0.15 0.20 0.25 0.30 0.35 0.40 WM 11 0.21 0.22 0.23 0.24 0.25 0.26 to Probability 0.0 0.2 0.4 0.6 0.8 1.0 Working Model 7 WM 8 WM 9 WM 10 WM 11 Toxicity target 1 2 3 4 5 6 Dose level NY 2009 13 / 21

Simulations (3) to Cumulative frequencies 0.0 0.2 0.4 0.6 0.8 1.0 WM 1 2 3 4 5 6 Cumulative frequencies 0.0 0.2 0.4 0.6 0.8 1.0 WM 7 8 9 10 11 0.0 0.1 0.2 0.3 0.4 0.0 0.1 0.2 0.3 0.4 Distance from the target Distance from the target Figure: Cumulative distribution of recommendation errors for 11 s NY 2009 14 / 21

Simulations (4) to For all scenarios and each, the percentage of correct selection were as follow 0.97, 0.92, 0.93, 0.97, 0.75, 0.89, 0.92, 0.94, 0.96, 0.95 and 0.61 respectively. Working Model d 1 d 2 d 3 d 4 d 5 d 6 WM 5 0.01 0.02 0.05 0.07 0.10 0.30 WM 11 0.21 0.22 0.23 0.24 0.25 0.26 NY 2009 15 / 21

Illustration to Retrospective analysis of the of the semisynthetic homoharringtonine trial Eighteen patients with advanced acute myeloid leukemia CRM logistic form with a fixed intercept of 3.0 Toxicity target 33% 5 dose levels: 0.5, 1, 3, 5 and 6 mg/m 2 /d 5 pseudo working doses -5.94, -5.20, -4.73, -3.71 and -3.00 At the end of the trial the MTD was selected to be the fourth dose levels Would the estimated MTD have been the same had we used a different model? *Levy et al.,br J Cancer 2006 ;95(3):253-9 NY 2009 16 / 21

Illustration to Dose d 1 d 2 d 3 d 4 d 5 Recommended dose n 18 (d i ) 3-3 12 - DLTs (t 18 (d i )) 0-1 4 - Estimated ˆR(d i ) by CRM 0.06 0.12 0.17 0.36 0.53 d 4 Empirical ˆR(d i ) 0-0.33 0.33 - Robustness Analysis Weights w 18 (d 1 ) w 18 (d 2 ) w 18 (d 3 ) w 18 (d 4 ) w 18 (d 5 ) Recommended dose Working Model 1 0.17 0.18 0.23 0.36 0.07 4 WM 2 0.17 0.18 0.34 0.27 0.05 3 WM 3 0.17 0.18 0.34 0.27 0.05 3 WM 4 0.17 0.18 0.20 0.41 0.04 4 WM 5 0.17 0.20 0.27 0.19 0.17 3 WM 6 0.17 0.18 0.34 0.27 0.04 4 WM 7 0.17 0.21 0.22 0.25 0.16 4 WM 8 0.17 0.20 0.24 0.24 0.16 3 WM 9 0.17 0.19 0.22 0.32 0.12 4 WM 10 0.17 0.20 0.23 0.22 0.18 3 WM 11 0.31 0.18 0.22 0.04 0.25 3 NY 2009 17 / 21

Illustration (2) to In this illustration, 5 s would have recommend the fourth dose level and 6 s would have recommend the third dose level at the end of the trial. NY 2009 18 / 21

Conclusions to Within the class of s chosen, the continual reassessment method is robust. We can make an approximate division of the class of all potential models into those which we consider to be reasonable models and those which are not. The here attempts to tie down in a more rigorous way the concept of being reasonable. A reasonable model is one that would exhibit good robustness properties. NY 2009 19 / 21