Schultz T W, Bearden A P, Jaworska J S
College of Veterinary Medicine, University of Tennessee, Knoxville 37901-1071, USA.
SAR QSAR Environ Res. 1996;5(2):99-112. doi: 10.1080/10629369608031710.
Toxicity values (log IGC50(-1)) for 60 phenols tested in the 2-d static population growth inhibition assay with the ciliate Tetrahymena pyriformis were tabulated. Each chemical was selected so the series formed uniform coverage of the hydrophobicity/ionization surface. A high quality hydrophobicity-dependent (log Kow) structure-toxicity relationship (log IGC50(-1) = 0.741 (log Kow)-1.433; n = 17; r2 = 0.970; s = 0.134; F = 486.55; Pr > F = 0.0001) was developed for phenols with pKa values > 9.8. Similarly, separate hydrophobicity-dependent relationships were developed for phenols with pKa values of 4.0, 5.1, 6.3, 7.5, and 8.7. Comparisons of intercepts and slopes, respectively, revealed phenols with pKa values of 6.3 to be the most toxic and the least influenced by hydrophobicity. These relationships were reversed for the more acidic and basic phenols. Plots of toxicity versus pKa for nitro-substituted phenols and phenols with log Kow values of either 1.75 or 2.50 further demonstrated bilinearity between toxicity and ionization. In an effort to more accurately model the relationship between toxicity and ionization, the absolute value function [6.3-pKa] was used to model ionization affects for derivatives with pKa values between 0 and 9.8. For derivatives with pKa value > 9.8, a value of 3.50 was used to quantitate ionization effects. The use of log Kow in conjunction with this modified pKa (delta pKa) resulted in the structure-toxicity relationship (log IGC(50)-1 = 0.567 (log Kow)-0.226 (delta pKa)-0.079; n = 54; r2 = 0.926; s = 0.215; F = 321.06; Pr > F = 0.0001). Derivatives with a nitro group in the 4-position typically did not model well with the above equation.
列出了在2天静态种群生长抑制试验中,用梨形四膜虫对60种酚进行测试的毒性值(log IGC50(-1))。选择每种化学品,以便该系列在疏水性/电离表面形成均匀覆盖。针对pKa值>9.8的酚类,建立了高质量的依赖疏水性(log Kow)的结构-毒性关系(log IGC50(-1)=0.741(log Kow)-1.433;n = 17;r2 = 0.970;s = 0.134;F = 486.55;Pr > F = 0.0001)。同样,针对pKa值为4.0、5.1、6.3、7.5和8.7的酚类分别建立了依赖疏水性的关系。分别对截距和斜率进行比较,结果显示pKa值为6.3的酚类毒性最大,且受疏水性影响最小。对于酸性和碱性更强的酚类,这些关系则相反。硝基取代酚以及log Kow值为1.75或2.50的酚类的毒性与pKa的关系图进一步证明了毒性与电离之间的双线性关系。为了更准确地模拟毒性与电离之间的关系,使用绝对值函数[6.3 - pKa]来模拟pKa值在0到9.8之间的衍生物的电离影响。对于pKa值>9.8的衍生物,使用3.50的值来定量电离影响。将log Kow与这种修正的pKa(δpKa)结合使用,得到了结构-毒性关系(log IGC(50)-1 = 0.567(log Kow)-0.226(δpKa)-0.079;n = 54;r2 = 0.926;s = 0.215;F = 321.06;Pr > F = 0.0001)。在4位带有硝基的衍生物通常不能很好地用上述方程进行模拟。