Noncancer Risk Assessment: Principles and Practice in Environmental and Occupational Settings

L. Haber, Joan E. Strawson, A. Maier, Irene M. Baskerville-Abraham, A. Parker, M. Dourson
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The issues raised by that publication are addressed later in this chapter. \n \n \n \nRecognizing both the historical approach and the importance of evaluation of MOA, this chapter will continue to use the term “noncancer risk,” but the methods described here should be understood to apply to both noncancer endpoints and cancer endpoints for which MOA information indicates that a threshold applies. This chapter describes the general framework for noncancer risk assessment and some salient principles for evaluating the quality of data and formulating judgments about the nature and magnitude of the hazard. Highlights of noncancer risk assessment methods used by a variety of agencies and organizations, and examples of how occupational risk assessment is moving toward a more systematic use of risk assessment principles are presented. \n \n \n \nThis chapter also has several specific aims. The first is to provide scientifically supportable quantitative risk assessment procedures to meet the risk assessment goals listed in the following paragraph. A second aim is to provide a scientific rationale that may be used to determine whether new quantitative risk assessment procedures not specifically examined in this chapter are scientifically supportable. The final aim of this chapter is to provide a basis for developing new or improved quantitative risk assessment procedures. \n \n \n \nThe quantitative risk assessment procedures described in this chapter have been developed to meet a variety of risk assessment goals. Although the protection of the public and occupational health are common themes that run through these separate risk assessment goals, the goals are sufficiently different to warrant separate and distinct procedures. 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引用次数: 12

Abstract

The approach to assessing the risks of noncancer toxicity has differed historically from that used to assess the potential risks of carcinogenicity. Assessment of risks of carcinogenicity has historically assumed that a small number of molecular events can evoke mutagenic changes in a single cell, ultimately leading to self-replicating damage and carcinogenicity. Generally, this is considered a nonthreshold effect because presumably all levels of exposure may pose a small, but finite, probability of generating a response. In contrast, it is most often assumed that noncarcinogenic changes have a threshold, a dose level below which a response is unlikely, because homeostatic, compensating, and adaptive mechanisms in the cell protect against toxic effects. Modern understanding of mode of action (MOA), loosely defined as how a chemical causes the observed effect, has led to refinements in this dichotomy. Rather than considering cancer versus noncancer effects, the focus is on whether or not the chemical causes its effects by a mutagenic MOA, specifically DNA interaction. Nonthreshold approaches are generally used for effects resulting from interaction with DNA, while effects resulting from a nonmutagenic MOA (including both cancer and noncancer endpoints) are generally evaluated using threshold approaches. A recent NRC publication [1], however, recommended linear extrapolation under certain conditions for noncancer endpoints that do not involved interaction with DNA. The issues raised by that publication are addressed later in this chapter. Recognizing both the historical approach and the importance of evaluation of MOA, this chapter will continue to use the term “noncancer risk,” but the methods described here should be understood to apply to both noncancer endpoints and cancer endpoints for which MOA information indicates that a threshold applies. This chapter describes the general framework for noncancer risk assessment and some salient principles for evaluating the quality of data and formulating judgments about the nature and magnitude of the hazard. Highlights of noncancer risk assessment methods used by a variety of agencies and organizations, and examples of how occupational risk assessment is moving toward a more systematic use of risk assessment principles are presented. This chapter also has several specific aims. The first is to provide scientifically supportable quantitative risk assessment procedures to meet the risk assessment goals listed in the following paragraph. A second aim is to provide a scientific rationale that may be used to determine whether new quantitative risk assessment procedures not specifically examined in this chapter are scientifically supportable. The final aim of this chapter is to provide a basis for developing new or improved quantitative risk assessment procedures. The quantitative risk assessment procedures described in this chapter have been developed to meet a variety of risk assessment goals. Although the protection of the public and occupational health are common themes that run through these separate risk assessment goals, the goals are sufficiently different to warrant separate and distinct procedures. Examples of such goals are as follows: to rank chemicals as to possible hazard; to prioritize chemicals for further evaluation, in combination with exposure information; to screen chemicals (e.g., new chemicals or ones under development), for purposes such as identifying which ones are appropriate for further development; to determine and/or estimate a level of daily exposure that is likely to be without an appreciable risk of deleterious effects during a lifetime; to determine and/or estimate the likely human response to exposure to various levels of a particular chemical or mixture. Moreover, differing amounts of toxicity data are needed for various quantitative procedures. Thus, both the problem being addressed and the amount of data available affect the choice of procedure. Keywords: benchmark dose; categorical regression; dose–response; dosimetry; hazard characterization; mode of action; physiologically based pharmacokinetic modeling; probabilistic RfD; problem formulation; risk characterization; uncertainty factor; weight of evidence
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非癌症风险评估:环境和职业环境中的原则和实践
评估非癌症毒性风险的方法历来不同于评估潜在致癌性风险的方法。对致癌性风险的评估历来假设,少数分子事件可以引起单个细胞的诱变变化,最终导致自我复制损伤和致癌性。一般来说,这被认为是一种非阈值效应,因为所有水平的暴露都可能造成很小但有限的产生反应的概率。相反,人们通常认为非致癌性变化有一个阈值,低于这个剂量水平就不可能产生反应,因为细胞中的稳态、补偿和适应性机制保护细胞免受毒性作用的影响。对作用方式(MOA)的现代理解,粗略地定义为一种化学物质如何引起所观察到的效果,使这种二分法得到了改进。而不是考虑癌症与非癌症的影响,重点是化学物质是否通过诱变的MOA引起其影响,特别是DNA相互作用。非阈值方法通常用于与DNA相互作用产生的效应,而非诱变MOA(包括癌症和非癌症终点)产生的效应通常使用阈值方法进行评估。然而,最近NRC的一份出版物[1]建议在某些条件下,对不涉及DNA相互作用的非癌症终点进行线性外推。该出版物提出的问题将在本章后面讨论。认识到历史方法和评估MOA的重要性,本章将继续使用术语“非癌症风险”,但这里描述的方法应被理解为既适用于非癌症终点,也适用于MOA信息表明适用阈值的癌症终点。本章描述了非癌症风险评估的一般框架,以及评估数据质量和制定有关危害性质和程度的判断的一些重要原则。重点介绍了各种机构和组织使用的非癌症风险评估方法,并举例说明了职业风险评估如何朝着更系统地使用风险评估原则的方向发展。本章还有几个具体的目的。第一是提供科学支持的定量风险评估程序,以实现下文所列的风险评估目标。第二个目的是提供一种科学依据,用于确定本章未具体审查的新的定量风险评估程序是否在科学上可支持。本章的最终目的是为开发新的或改进的定量风险评估程序提供基础。本章中描述的定量风险评估程序是为了满足各种风险评估目标而开发的。尽管保护公众健康和职业健康是贯穿这些单独的风险评估目标的共同主题,但这些目标差别很大,有必要采取单独和不同的程序。这些目标的例子如下:根据可能的危害对化学品进行排序;结合接触信息,优先考虑进一步评价的化学品;筛选化学品(例如新化学品或正在开发的化学品),以确定哪些化学品适合进一步发展;确定和/或估计在一生中可能不会有明显有害影响风险的每日暴露水平;确定和/或估计人体暴露于不同水平的特定化学品或混合物时可能产生的反应。此外,不同的定量程序需要不同数量的毒性数据。因此,要解决的问题和可用数据的数量都会影响程序的选择。关键词:基准剂量;分类回归;剂量反应;剂量测定法;风险特征;作用方式;基于生理的药代动力学建模;概率RfD;问题制定;风险特征;不确定性因素;证据的重要性
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