Watanabe K, Bois F Y, Zeise L
Reproductive and Cancer Hazard Assessment Section, California Environmental Protection Agency, Berkeley 94704.
Risk Anal. 1992 Jun;12(2):301-10. doi: 10.1111/j.1539-6924.1992.tb00677.x.
We reanalyze the acute toxicity data on cancer chemotherapeutic agents compiled by Freireich et al.(1) and Schein et al.(2) to derive coefficients of the allometric equation for scaling toxic doses across species (toxic dose = a.[body weight]b). In doing so, we extend the analysis of Travis and White (Risk Analysis, 1988, 8, 119-125) by addressing uncertainties inherent in the analysis and by including the hamster data, previously not used. Through Monte Carlo sampling, we specifically account for measurement errors when deriving confidence intervals and testing hypotheses. Two hypotheses are considered: first, that the allometric scaling power (b) varies for chemicals of the type studied; second, that the same scaling power, or "scaling law," holds for all chemicals in the data set. Following the first hypothesis, in 95% of the cases the allometric power of body weight falls in the range from 0.42-0.97, with a population mean of 0.74. Assuming the second hypothesis to be true-that the same scaling law is followed for all chemicals-the maximum likelihood estimate of the scaling power is 0.74; confidence bounds on the mean depend on the size of measurement error assumed. Under a "best case" analysis, 95% confidence bounds on the mean are 0.71 and 0.77, similar to the results reported by Travis and White. For alternative assumptions regarding measurement error, the confidence intervals are larger and include 0.67, but not 1.00. Although a scaling power of about 0.75 provides the best fit to the data as a whole, a scaling power of 0.67, corresponding to scaling per unit surface area, is not rejected when the nonhomogeneity of variances is taken into account. Hence, both surface area and 0.75 power scaling are consistent with the Freireich et al. and Schein et al. data sets. To illustrate the potential impact of overestimating the scaling power, we compare reported human MTDs to values extrapolated from mouse LD10s.
我们重新分析了由弗雷赖希等人(1)和沙因等人(2)汇编的癌症化疗药物急性毒性数据,以得出用于跨物种缩放毒性剂量的异速生长方程系数(毒性剂量 = a·[体重]b)。在此过程中,我们扩展了特拉维斯和怀特的分析(《风险分析》,1988年,第8卷,第119 - 125页),解决了分析中固有的不确定性,并纳入了先前未使用的仓鼠数据。通过蒙特卡罗抽样,我们在推导置信区间和检验假设时专门考虑了测量误差。考虑了两个假设:第一,所研究类型的化学物质的异速生长缩放指数(b)有所不同;第二,数据集中所有化学物质遵循相同的缩放指数,即“缩放定律”。按照第一个假设,在95%的情况下,体重的异速生长指数落在0.42 - 0.97范围内,总体均值为0.74。假设第二个假设为真,即所有化学物质遵循相同的缩放定律,缩放指数的最大似然估计值为0.74;均值的置信区间取决于所假设的测量误差大小。在“最佳情况”分析下,均值的95%置信区间为0.71和0.77,与特拉维斯和怀特报告的结果相似。对于关于测量误差的其他假设,置信区间更大,包括0.67,但不包括1.00。尽管约0.75的缩放指数总体上最适合数据,但当考虑方差的非齐次性时,对应于单位表面积缩放的0.67缩放指数并未被拒绝。因此,表面积缩放和0.75指数缩放都与弗雷赖希等人和沙因等人的数据集一致。为了说明高估缩放指数的潜在影响,我们将报告的人类最大耐受剂量与从小鼠LD10外推的值进行了比较。