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通过运用特定知识取代默认选项来降低风险评估中的不确定性。

Reducing uncertainty in risk assessment by using specific knowledge to replace default options.

作者信息

McClellan R O

机构信息

Chemical Industry Institute of Toxicology, Research Triangle Park, North Carolina 27709, USA.

出版信息

Drug Metab Rev. 1996 Feb-May;28(1-2):149-79. doi: 10.3109/03602539608993997.

Abstract

This paper has advocated the development of specific scientific information, especially information on the mechanisms of action of chemicals, to use in place of default options in assessing human cancer risks. Four examples have been discussed that build largely on information from the CIIT research program. These four examples are worthy of consideration as a group, with a view to developing insights for increasing the effectiveness and efficiency of obtaining such data in the future and, most of all, to increase their acceptance for use instead of default options. In my view, key features of all four examples are that the data are framed within an exposure-dose-response paradigm and that there is a clear linkage to the end point of concern-cancer. As the number of techniques available for making observations at the cellular and molecular levels continues to increase at a rapid pace, linking these observations to the health end points of concern such as cancer is going to be increasingly important, especially in enhancing the value of the observations for risk assessment purposes. Equally as important, the mechanistic observations must be linked to realistic exposures and associated tissue dose that can be related to realistic human exposure scenarios. In my opinion, the likelihood of obtaining information of value for risk assessment purposes using the most sophisticated of molecular and cellular techniques will be of limited value if the exposures or doses are not realistically linked to those likely to be encountered by humans. The mechanism of alpha 2u-globulin nephropathy and its association with kidney tumors in male rats and the conclusion that the male rat kidney tumor findings are not applicable to assessing human cancer risk is an example of a qualitative decision. I suspect this may be a somewhat unusual case. As one looks across the various mammalian species used for experimentation and makes comparisons with humans, a unifying theme is the relative abundance of similarities. Indeed, this is a major argument for the use of laboratory animals to obtain information relevant to humans. Nonetheless, vigilance to differences among species is important. When differences are observed, we must capitalize on them to better understand the underlying biological mechanisms that mediate the differences. If, as I have suggested, laboratory animal species are more like than different from humans in their basic biological characteristics, there is a rationale for continuing to use laboratory animals as sources of data to help assess human risks of exposure to chemicals. It follows from this that quantitative differences among species such as observed with both formaldehyde and 1,3-butadiene assume major importance for assessing human risks. In my opinion, quantitation of the likely human carcinogenic potency of chemicals is of major importance. It is not sufficient to simply classify chemicals with regard to the likelihood of their being human carcinogens, as done by IARC (1994) and U.S. EPA (1986). IARC has placed more than 60 chemicals or processes (such as coke production) in group 1, carcinogenic to humans; more than 50 in group 2a, probably carcinogenic to humans; and 250 in group 2b, possibly carcinogenic to humans. This rank order implies differing levels of concern for three categories. However, even this rough three-bin system does not convey a very clear picture as to the degree of concern that should be accorded a given chemical for producing cancer. For example, the chemicals categorized as group 1, human carcinogens, using potency estimates developed by the U.S. EPA differ in potency by roughly 4 orders of magnitude. For example, a lifetime cancer risk is 6.2 x 10(-2) per micrograms/m3 for bischloromethyl ether and 8.3 x 10(-6) for benzene (NRC, 1994). Differences such as this offer strong arguments for complementing simplistic hazard identification schemes such as the IARC and EPA carcinogen classification systems w

摘要

本文主张开发特定的科学信息,尤其是关于化学物质作用机制的信息,以用于在评估人类癌症风险时替代默认选项。文中讨论了四个主要基于化学工业毒理研究所(CIIT)研究项目信息的例子。这四个例子作为一个整体值得考虑,目的是深入了解如何提高未来获取此类数据的有效性和效率,最重要的是,提高它们被接受用于替代默认选项的程度。在我看来,所有这四个例子的关键特征在于,数据是在暴露 - 剂量 - 反应范式内构建的,并且与所关注的终点——癌症有明确的联系。随着在细胞和分子水平进行观察的可用技术数量持续快速增加,将这些观察结果与诸如癌症等所关注的健康终点联系起来将变得越来越重要,特别是在提高这些观察结果对风险评估目的的价值方面。同样重要的是,机制性观察结果必须与现实的暴露以及相关的组织剂量相联系,而这些剂量可以与现实的人类暴露情况相关联。在我看来,如果暴露或剂量与人类可能遇到的情况没有实际联系,那么使用最复杂的分子和细胞技术获取对风险评估有价值的信息的可能性将很有限。α2u - 球蛋白肾病的机制及其与雄性大鼠肾肿瘤的关联,以及雄性大鼠肾肿瘤研究结果不适用于评估人类癌症风险的结论就是一个定性决策的例子。我怀疑这可能是一个有点不寻常的情况。当人们审视用于实验的各种哺乳动物物种并与人类进行比较时,一个统一的主题是相似之处相对丰富。事实上,这是使用实验动物获取与人类相关信息的一个主要论据。尽管如此,对物种间差异保持警惕很重要。当观察到差异时,我们必须利用它们来更好地理解介导这些差异的潜在生物学机制。如果正如我所指出的,实验动物物种在其基本生物学特征上与人类的相似之处多于差异,那么就有理由继续将实验动物作为数据来源,以帮助评估人类接触化学物质的风险。由此可知,甲醛和1,3 - 丁二烯等物种间的定量差异对于评估人类风险具有重要意义。在我看来,对化学物质可能的人类致癌潜力进行定量至关重要。仅仅像国际癌症研究机构(IARC,1994年)和美国环境保护局(EPA,1986年)那样简单地对化学物质作为人类致癌物的可能性进行分类是不够的。IARC已将60多种化学物质或过程(如焦炭生产)列为第1组,对人类致癌;50多种列为第2A组,可能对人类致癌;250种列为第2B组,可能对人类致癌。这种排名顺序意味着对这三个类别有不同程度的关注。然而,即使是这种粗略的三分系统也没有非常清晰地表明对于一种给定化学物质导致癌症应给予何种程度的关注。例如,根据美国环境保护局制定的效力估计,被归类为第1组人类致癌物的化学物质,其效力相差约4个数量级。例如,双氯甲醚的终生癌症风险为每微克/立方米6.2×10⁻²,而苯为8.3×10⁻⁶(美国国家研究委员会,1994年)。诸如此类的差异有力地证明了需要补充像IARC和EPA致癌物分类系统这样简单的危害识别方案。

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