Chen H F, Hee S S
Department of Environmental Health Sciences, UCLA Center for Occupational and Environmental Health, University of California, Los Angeles School of Public Health 90024-1772, USA.
Ecotoxicol Environ Saf. 1995 Mar;30(2):120-3. doi: 10.1006/eesa.1995.1014.
The Microtox EC50 values for the following ketones are reported in the following homologous series: straight chain methyl ketones (acetone, 2-butanone, 2-pentanone, 2-hepatonone, 2-octanone, 2-decanone, and 2-tridecanone); methyl ketones substituted at one alpha carbon (3-methyl-2-butanone; 3,3-dimethyl-2-butanone); methyl substituted at two alpha carbons (2,4-dimethyl-3-pentanone; 2,2,4,4-tetramethyl-3-pentanone); phenyl groups replacing methyl in acetone (acetophenone; benzophenone); methyl groups substituted at the alpha carbons of cyclohexanone; and 2,3- 2,4-, and 2,5-hexanediones, most for the first time. While there were linear relationships between log EC50 and MW for the straight chain methyl ketones, and for methyl substitution at the alpha carbon for methyl ketones, there were no other linear relationships. As molecular weight increased, the EC50 values of soluble ketones decreased; as distance between two carbonyl groups decreased so too did EC50 values. Thus, for the ketones the geometry around the carbonyl group is an important determinant of toxicity as well as MW, water solubility, and octanol/water coefficient.
以下酮类化合物的微毒性半数有效浓度(EC50)值在以下同系物系列中报告:直链甲基酮(丙酮、2-丁酮、2-戊酮、2-庚酮、2-辛酮、2-癸酮和2-十三烷酮);在一个α-碳上被取代的甲基酮(3-甲基-2-丁酮;3,3-二甲基-2-丁酮);在两个α-碳上被取代的甲基(2,4-二甲基-3-戊酮;2,2,4,4-四甲基-3-戊酮);在丙酮中取代甲基的苯基(苯乙酮;二苯甲酮);在环己酮的α-碳上被取代的甲基;以及2,3-、2,4-和2,5-己二酮,其中大多数是首次报道。虽然直链甲基酮以及甲基酮在α-碳上的甲基取代的log EC50与分子量之间存在线性关系,但不存在其他线性关系。随着分子量增加,可溶性酮的EC50值降低;随着两个羰基之间的距离减小,EC50值也降低。因此,对于酮类化合物,羰基周围的几何结构以及分子量、水溶性和正辛醇/水系数都是毒性的重要决定因素。