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Principles of risk assessment for determining the safety of chemicals: Recent assessment of residual solvents in drugs and di(2-ethylhexyl) phthalate.

机译:确定化学品安全性的风险评估原则:药物和邻苯二甲酸二(2-乙基己基)酯中残留溶剂的最新评估。

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ABSTRACT Risk assessment of chemicals is essential for the estimation of chemical safety, and animal toxicity data are typically used in the evaluation process, which consists of hazard identification, dose-response assessment, exposure assessment, and risk characterization. Hazard identification entails the collection of all available toxicity data and assessment of toxicity endpoints based on findings for repeated dose toxicity, carcinogenicity or genotoxicity and species-specificity. Once a review is compiled, the allowable lifetime exposure level of a chemical is estimated from a dose-response assessment based on several measures. For non-carcinogens and non-genotoxic carcinogens, the no-observed-adverse-effect-level (NOAEL) is divided by uncertainty factors (e.g. with environmental pollutants) or safety factors (e.g. with food additives) to derive a tolerable daily intake (TDI) or acceptable daily intake (ADI), respectively. These factors include interspecies and individual differences, duration of exposure, quality of data, and nature of toxicity such as carcinogenicity or neurotoxicity. For genotoxic carcinogens, low dose extrapolation is accomplished with mathematical modeling (e.g. linearized multistage model) from the point of departure to obtain exposure levels that will be associated with an excess lifetime cancer risk of a certain level. Data for levels of chemicals in food, water and air, are routinely used for exposure assessment. Finally, risk characterization is performed to ensure that the established 'safe' level of exposure exceeds the estimated level of actual exposure. These principles have led to the evaluation of several existing chemicals. To establish a guideline for residual solvents in medicine, the permitted daily exposure (PDE), equivalent to TDI, of N,N-dimethylformamide was derived on the basis of developmental toxicity (malformation) and of N-methylpyrrolidone on the basis of the developmental neurotoxicity. A TDI for di(2-ethylhexyl)phthalate was derived from assessment of testicular toxicity.
机译:摘要化学品的风险评估对于评估化学品的安全性至关重要,评估过程中通常使用动物毒性数据,其中包括危害识别,剂量反应评估,暴露评估和风险表征。危害识别需要收集所有可用的毒性数据,并根据重复剂量毒性,致癌性或遗传毒性和物种特异性的发现评估毒性终点。编制完审查后,可基于几种措施,通过剂量反应评估来估算化学物质的允许使用寿命。对于非致癌物和非遗传毒性致癌物,将未观察到的不良影响水平(NOAEL)除以不确定性因素(例如,环境污染物)或安全因素(例如,食品添加剂),以得出可耐受的每日摄入量( TDI)或可接受的每日摄入量(ADI)。这些因素包括种间和个体差异,暴露时间,数据质量以及毒性(例如致癌性或神经毒性)的性质。对于遗传毒性致癌物,从出发点开始通过数学建模(例如线性化多阶段模型)完成低剂量外推,以获得与一定水平的终身终生癌症风险相关的暴露水平。食物,水和空气中化学物质含量的数据通常用于暴露评估。最后,进行风险表征以确保已建立的“安全”暴露水平超过了实际暴露的估计水平。这些原则导致对几种现有化学品的评估。为了建立药物中残留溶剂的指南,根据发育毒性(畸形)得出N,N-二甲基甲酰胺的每日允许暴露量(PDE),相当于TDI,根据发育毒性得出N-甲基吡咯烷酮的每日允许暴露量。神经毒性。邻苯二甲酸二(2-乙基己基)酯的TDI来自睾丸毒性的评估。

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