Calleja M C, Geladi P, Persoone G
Laboratory for Biological Research in Aquatic Pollution, University of Ghent, Belgium.
Food Chem Toxicol. 1994 Oct;32(10):923-41. doi: 10.1016/0278-6915(94)90091-4.
Linear and non-linear modelling of human acute toxicity (as human lethal concentrations; HLCs) of the 38 organic chemicals from the 50 priority compounds of the Multicentre Evaluation of In Vitro Cytotoxicity (MEIC) programme was investigated. The models obtained were derived either from a set of 23 physicochemical properties of the compounds or from their acute toxicities to five aquatic non-vertebrates together with the physicochemical properties. For the linear type, modelling was performed using a partial least square projection to latent structures (PLS) regression method; for the non-linear models, both PLS regression and neural network were utilized. A neural network using a combination of backpropagation and cascade-correlation algorithms was applied in this study. The results generally reveal a slightly better predictive performance of the models obtained from PLS regression than those obtained from neural networks. However, the model composed of physicochemical properties (PC-model) from the trained neural network using a back propagation algorithm with pruning technique proved superior to that trained with a combination of backpropagation and cascade-correlation algorithms after leave-one-out cross-validation. The predictive power of the PC-models, whether linear or non-linear, was comparable with that of the corresponding models consisting of both structural descriptors and the ecotoxicological tests (ECOPC-models), except for the battery (ECOPC-model) from the neural network. The composition of the 'best' PLS and neural network models points to the importance of the combination of physicochemical properties reflecting lipophilicity, size, volume, intermolecular binding forces and electronic properties of the molecule. All the aquatic non-vertebrate tests are shown to be essential in explaining human acute toxicity. However, the degree of contribution differed, with the crustacean (Artemia salina) and the bacterial (Microtox) bioassays being more important to the linear and non-linear PLS models, whereas the crustacean (Artemia salina and Streptocephalus proboscideus) tests, and the rotifer (Brachionus calyciflorus) assay were important to the neural network models. The organochlorine (lindane) and bipyridinium (paraquat) pesticides were common outliers in all the models. Moreover, the latter two compounds and the organophosphate (malathion) pesticide were also common outliers in all ECOPC-models. Other types of pesticides, however, fit the models. The predicted HLCs of a number of non-pesticides, including some chlorinated compounds, also deviated from the observed HLCs by more than one order of magnitude.
对多中心体外细胞毒性评估(MEIC)计划中50种优先化合物里38种有机化学品的人体急性毒性(以人体致死浓度;HLCs表示)进行了线性和非线性建模研究。所获得的模型要么源自一组23种化合物的物理化学性质,要么源自它们对五种水生无脊椎动物的急性毒性以及物理化学性质。对于线性模型,使用偏最小二乘投影到潜在结构(PLS)回归方法进行建模;对于非线性模型,则同时使用PLS回归和神经网络。本研究应用了一种结合反向传播和级联相关算法的神经网络。结果总体显示,PLS回归得到的模型预测性能略优于神经网络得到的模型。然而,在留一法交叉验证后,由使用带有剪枝技术的反向传播算法训练的神经网络得到的由物理化学性质组成的模型(PC模型),被证明优于由反向传播和级联相关算法结合训练的模型。PC模型(无论是线性还是非线性)的预测能力与由结构描述符和生态毒理学测试组成的相应模型(ECOPC模型)相当,但神经网络的一组测试(ECOPC模型)除外。“最佳”PLS和神经网络模型的组成表明,反映分子亲脂性、大小、体积、分子间结合力和电子性质的物理化学性质组合很重要。所有水生无脊椎动物测试对于解释人体急性毒性都至关重要。然而,贡献程度有所不同,甲壳类动物(卤虫)和细菌(Microtox)生物测定对线性和非线性PLS模型更为重要,而甲壳类动物(卤虫和长鼻巨头水蚤)测试以及轮虫(萼花臂尾轮虫)测定对神经网络模型很重要。有机氯(林丹)和联吡啶(百草枯)农药在所有模型中都是常见的异常值。此外,后两种化合物和有机磷(马拉硫磷)农药在所有ECOPC模型中也是常见的异常值。然而,其他类型的农药符合模型。一些非农药化合物(包括一些氯化化合物)的预测HLCs与观察到的HLCs也相差一个以上数量级。