己酸二乙氨基乙醇酯的致突变性研究

采用鼠伤寒沙门氏菌回复突变试验(Ames试验),用TA97,TA98,TA100和TA102菌株,加与不加S9,剂量分别设为每皿1000μg,500μg和250μg;小鼠骨髓多染红细胞微核试验,剂量设为雄性、雌性小鼠给药剂量均为250,500和1000mg·kg-1;小鼠睾丸精母细胞染色体畸变试验,剂量设为625mg·kg-1,1250mg·kg-1和2500mg·kg-1.结果表明,Ames试验中,各测试浓度的诱发回变菌落数均未超过自发回变菌落数的2倍;小鼠骨髓多染红细胞微核试验和小鼠睾丸精母细胞染色体畸变试验,各剂量组和溶剂对照组的微核率进行统计学处理,未见有显着性差异(P>0.05),表明各项试验结果均为阴性.因此,己酸二乙氨基乙醇酯无致突变作用.     

A model based on molecular structure descriptors for predicting mutagenicity of organic compounds

A model predictive of the potential mutagenicity of organic compounds was devised by relating mutagenicity data obtained in the Ames reversion test to molecular structure parameters describing their hydrophobic, topological, steric and electronic properties. These included second order valence molecular connectivity index, parachor, molar refraction and polarizability of electrons. A classification rule was calculated, by means of discriminant analysis, using a training set of 117 compounds of various chemical classes. There was agreement between experimental data and theoretical expectations for the majority of compounds (70.9%), with homogeneous figures among the different chemical classes under scrutiny. An exception was represented by halogenated aliphatics with up to 3 C atoms, the mutagenicity of which was poorly predicted by the structural analysis model.     

Assessment of mutagenic potency of source water treated by ozone and adsorption processes

This research utilized the Ames test to determine the mutagenicity of water treated by advanced processes, including ozonation and granular activated carbon (GAC). Raw water samples for this research included those obtained from the Pan Hsin waterworks as well as samples containing humic acids. Treated samples were collected from the pilot‐scale advanced treatment plant. The Ames test was used to measure the mutagenicity of the water after each treatment process. For the Pan Hsin raw water samples treated with ozone or GAC, it was indicated that, regardless of whether samples were preozonated or not, they all showed a mutagenic potency less than 2 once the S9 enzyme was added. This level of mutagenicity is insignificant. The prepared humic acid samples, on the other hand, demonstrated a significant reduction in mutagenicity after the pre‐ozonation process, indicating that preozonation can lower the degree of mutagenicity. Furthermore, the mutagenicity of the prepared humic acid samples gradually decreased after the advanced treatment process. However, when chlorine was added later to these samples, the mutagenicity increased again. This research shows that the use of O3/GAC processes to treat water can successfully lower mutagenicity, indicating a great potential for applications in the treatment of drinking water.     

Genotoxicity study of phenol and o-cresol using the micronucleus test and the comet assay

Phenol and cresols are common toxic environmental pollutants. In this study, the micronucleus assay and the alkaline single cell gel electrophoresis (SCGE) technique have been used to investigate the genotoxic activity of phenol and o-cresol. The result of experiments revealed that phenol and o-cresol were both evident genotoxins, and the genotoxic activity of o-cresol was stronger. In the micronucleus assay, phenol and o-cresol could both cause a significant increase in the micronucleus (MN) frequencies (p?p?p?p?相似文献   

Induction of gene mutations in salmonella and Drosophila by soluble Cr(Vi) compounds: Synergistic effects of nitrilotriacetic acid

The interaction between NTA and soluble Cr(VI) (K₂Cr₂O₇) was studied by the Ames test on S. typhimurium and the sex‐linked recessive lethal test on D. melanogaster. In both systems a synergistic effect of NTA on Cr(VI) mutagenicity took place at sub‐toxic doses of Cr(VI). The synergism could depend on the action of NTA on intracellular Cr(VI) reduction, as more Cr(VI) was reduced in vitro to Cr(III) by Salmonella and Drosophila protein extracts in the presence of NTA. A similar enhancement of soluble Cr(VI) mutagenicity was produced by low doses of EDTA.