Kroes R, Galli C, Munro I, Schilter B, Tran L, Walker R, Würtzen G
RITOX-Utrecht University, Faculty of Veterinary Medicine, PO Box 80176, 3508 TD Utrecht, The Netherlands.
Food Chem Toxicol. 2000 Feb-Mar;38(2-3):255-312. doi: 10.1016/s0278-6915(99)00120-9.
The de minimis concept acknowledges a human exposure threshold value for chemicals below which there is no significant risk to human health. It is the underlying principle for the US Food and Drug Administration (FDA) regulation on substances used in food-contact articles. Further to this, the principle of Threshold of Toxicological Concern (TTC) has been developed and is now used by the Joint FAO/WHO Expert Committee on Food Additives (JECFA) in their evaluations. Establishing an accepted TTC would benefit consumers, industry and regulators, since it would preclude extensive toxicity evaluations when human intakes are below such threshold, and direct considerable time and cost resources towards testing substances with the highest potential risk to human health. It was questioned, however, whether specific endpoints that may potentially give rise to low-dose effects would be covered by such threshold. In this review, the possibility of defining a TTC for chemical substances present in the diet was examined for general toxicity endpoints (including carcinogenicity), as well as for specific endpoints, namely neurotoxicity and developmental neurotoxicity, immunotoxicity and developmental toxicity. For each of these endpoints, a database of specific no-observed-effect levels (NOELs) was compiled by screening oral toxicity studies. The substances recorded in each specific database were selected on the basis of their demonstrated adverse effects. For the neurotoxicity and developmental neurotoxicity databases, it was intended to cover all classes of compounds reported to have either a demonstrated neurotoxic or developmentally neurotoxic effect, or at least, on a biochemical or pharmacological basis were considered to have a potential for displaying such effects. For the immunotoxicity endpoint, it was ensured that only immunotoxicants were included in the database by selecting most of the substances from the Luster et al. database, provided that they satisfied the criteria for immunotoxicity defined by Luster. For the developmental toxicity database, substances were selected from the Munro et al. database that contained the lowest NOELs retrieved from the literature for more than 600 compounds. After screening these, substances showing any effect which could point to developmental toxicity as broadly defined by the US were recorded in the database. Additionally, endocrine toxicity and allergenicity were addressed as two separate cases, using different approaches and methodology. The distributions of NOELs for the neurotoxicity, developmental neurotoxicity and developmental toxicity endpoints were compared with the distribution of NOELs for non-specific carcinogenic endpoints. As the immunotoxicity database was too limited to draw such a distribution of immune NOELs, the immunotoxicity endpoint was evaluated by comparing immune NOELs (or LOELs-lowest-observed-effect levels-when NOELs were not available) with non-immune NOELs (or LOELs), in order to compare the sensitivity of this endpoint with non-specific endpoints. A different methodology was adopted for the evaluation of the endocrine toxicity endpoint since data currently available do not permit the establishment of a clear causal link between endocrine active chemicals and adverse effects in humans. Therefore, this endpoint was analysed by estimating the human exposure to oestrogenic environmental chemicals and evaluating their potential impact on human health, based on their contribution to the overall exposure, and their estrogenic potency relative to endogenous hormones. The allergenicity endpoint was not analysed as such. It was addressed in a separate section because this issue is not relevant to the overall population but rather to subsets of susceptible individuals, and allergic risks are usually controlled by other means (i.e. labelling) than the Threshold of Toxicological Concern approach. (ABSTRACT TRUNCATED)
微量概念承认化学品存在一个人体接触阈值,低于该阈值对人体健康无显著风险。这是美国食品药品监督管理局(FDA)对食品接触制品中使用物质的监管的基本原则。除此之外,毒理学关注阈值(TTC)原则已得到发展,目前联合国粮食及农业组织/世界卫生组织食品添加剂联合专家委员会(JECFA)在其评估中使用该原则。确立一个公认的TTC将使消费者、行业和监管机构受益,因为当人体摄入量低于该阈值时,可避免进行广泛的毒性评估,并将大量时间和成本资源用于对人体健康潜在风险最高的物质进行检测。然而,有人质疑这样的阈值是否涵盖可能产生低剂量效应的特定终点。在本综述中,针对一般毒性终点(包括致癌性)以及特定终点,即神经毒性和发育神经毒性、免疫毒性和发育毒性,研究了为饮食中存在的化学物质定义TTC的可能性。对于这些终点中的每一个,通过筛选口服毒性研究编制了特定未观察到效应水平(NOELs)的数据库。每个特定数据库中记录的物质是根据其已证实的不良反应选择的。对于神经毒性和发育神经毒性数据库,旨在涵盖所有已报告具有神经毒性或发育神经毒性效应的化合物类别,或者至少在生化或药理学基础上被认为具有显示此类效应潜力的化合物类别。对于免疫毒性终点,通过从Luster等人的数据库中选择大多数物质来确保数据库中仅包含免疫毒物,前提是它们满足Luster定义的免疫毒性标准。对于发育毒性数据库,从Munro等人包含从文献中检索到的600多种化合物的最低NOELs的数据库中选择物质。筛选这些物质后,将显示任何可指向美国广泛定义的发育毒性效应的物质记录在数据库中。此外,使用不同的方法和手段将内分泌毒性和致敏性作为两个单独的情况进行处理。将神经毒性、发育神经毒性和发育毒性终点NOELs的分布与非特异性致癌终点NOELs的分布进行比较。由于免疫毒性数据库过于有限,无法得出免疫NOELs的这种分布,因此通过将免疫NOELs(或当没有NOELs时的最低观察到效应水平(LOELs))与非免疫NOELs(或LOELs)进行比较来评估免疫毒性终点,以便将该终点的敏感性与非特异性终点进行比较。对于内分泌毒性终点的评估采用了不同的方法,因为目前可用的数据不允许在环境内分泌活性化学物质与人类不良反应之间建立明确的因果联系。因此,通过估计人体对雌激素环境化学物质的接触并评估它们对人体健康的潜在影响来分析该终点,基于它们对总体接触的贡献以及它们相对于内源性激素的雌激素效力。致敏性终点未作此类分析。在单独的一节中讨论了该问题,因为这个问题与总体人群无关,而是与易感个体子集有关,并且过敏风险通常通过其他手段(即标签)而非毒理学关注阈值方法来控制。(摘要截断)