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. Author manuscript; available in PMC: 2022 Aug 31.
Published in final edited form as: Environmetrics. 2020 May 16;31(7):e2630. doi: 10.1002/env.2630

TABLE 3.

The cell proliferation data with full design

Model a b c d ζ σ BMD BMDL BMDU AIC Weight
Exp 7.285 (0.097) 0.322 (0.085) 1.388 (0.040) 1.012 (0.228) 0.394 (0.043) 0.083 (0.065) 0.025 0.333 50.859 0.197
Inv Exp 7.284 (0.097) 1.696 (0.478) 1.654 (0.289) 0.434 (0.188) 0.400 (0.044) 0.125 (0.085) 0.091 0.449 52.207 0.101
Hill 7.288 (0.098) 2.937 (0.931) 1.435 (0.075) 1.1524 (0.334) 0.396 (0.043) 0.098 (0.081) 0.014 0.401 51.447 0.147
LN 7.289 (0.097) 0.525 (0.111) 1.445 (0.099) 0.646 (0.204) 0.397 (0.043) 0.122 (0.087) 0.017 0.439 51.738 0.127
Logistic 0.949 (0.100) 0.420 (0.107) 10.103 (0.237) 0.956 (0.214) 0.393 (0.043) 0.077 ( 0.061) 0.011 0.320 50.758 0.208
Probit 0.588 (0.057) 0.245 (0.061) 10.089 (0.226) 0.920 (0.197) 0.393 (0.043) 0.071 (0.057) 0.011 0.306 50.647 0.220
The direct approach: standard errors estimate (23) and Wald-type limits 0.091 (0.073) 0.014 0.409
The direct approach: bootstrap standard error and percentile limits 0.091 (0.103) 0.011 0.325
The indirect approach: bootstrap standard error and percentile limits 0.091 (0.101) 0.019 0.318

Note: Estimates for all fitted models (with one representative for nested models), the model-specific BMD estimates, 90% profile likelihood based BMDL and BMDU, corrected AIC, and corresponding weight for averaging. Model-averaged BMD estimates based on the direct approach with 90% Wald and percentile bootstrap BMDL and BMDU limits, and based on the indirect approach with 90% percentile bootstrap BMDL and BMDU limits. Estimates for the standard error are shown: using formula (23) and the bootstrap for the direct estimate and only the bootstrap for the indirect estimate. B = 3, 000 bootstrap samples were generated.

Abbreviations: Exp, exponential; Inv Exp, inverse exponential; LN, log-normal; LSN, log-skew-normal model.