Melnick Ronald L, Thayer Kristina A, Bucher John R
National Institute of Environmental Health Sciences, National Institutes of Health, Department of Health and Human Services, Research Triangle Park, NC 27709, USA.
Environ Health Perspect. 2008 Jan;116(1):130-5. doi: 10.1289/ehp.9989.
Conflicting views have been expressed frequently on assessments of human cancer risk of environmental agents based on animal carcinogenicity data; this is primarily because of uncertainties associated with extrapolations of toxicologic findings from studies in experimental animals to human circumstances. Underlying these uncertainties are issues related to how experiments are designed, how rigorously hypotheses are tested, and to what extent assertions extend beyond actual findings. National and international health agencies regard carcinogenicity findings in well-conducted experimental animal studies as evidence of potential carcinogenic risk to humans. Controversies arise when both positive and negative carcinogenicity data exist for a specific agent or when incomplete mechanistic data suggest a possible species difference in response. Issues of experimental design and evaluation that might contribute to disparate results are addressed in this article. To serve as reliable sources of data for the evaluation of the carcinogenic potential of environmental agents, experimental studies must include a) animal models that are sensitive to the end points under investigation; b) detailed characterization of the agent and the administered doses; c) challenging doses and durations of exposure (at least 2 years for rats and mice); d) sufficient numbers of animals per dose group to be capable of detecting a true effect; e) multiple dose groups to allow characterization of dose-response relationships, f) complete and peer-reviewed histopathologic evaluations; and g) pairwise comparisons and analyses of trends based on survival-adjusted tumor incidence. Pharmacokinetic models and mechanistic hypotheses may provide insights into the biological behavior of the agent; however, they must be adequately tested before being used to evaluate human cancer risk.
基于动物致癌性数据对环境因子的人类癌症风险评估,人们频繁表达了相互矛盾的观点;这主要是因为将实验动物研究中的毒理学发现外推至人类情况存在不确定性。这些不确定性的背后,是与实验设计方式、假设检验的严格程度以及断言超出实际发现的程度相关的问题。国家和国际卫生机构将精心开展的实验动物研究中的致癌性发现视为对人类潜在致癌风险的证据。当针对某一特定因子同时存在阳性和阴性致癌性数据,或者不完整的机制数据表明可能存在种属反应差异时,争议就会出现。本文探讨了可能导致不同结果的实验设计和评估问题。为了作为评估环境因子致癌潜力的可靠数据来源,实验研究必须包括:a) 对所研究终点敏感的动物模型;b) 对因子和给药剂量的详细表征;c) 具有挑战性的剂量和暴露持续时间(大鼠和小鼠至少2年);d) 每个剂量组有足够数量的动物以能够检测到真实效应;e) 多个剂量组以表征剂量反应关系;f) 完整且经过同行评审的组织病理学评估;g) 基于生存调整后的肿瘤发生率进行成对比较和趋势分析。药代动力学模型和机制假设可能有助于深入了解因子的生物学行为;然而,在用于评估人类癌症风险之前,它们必须经过充分检验。