Toxicology, Health-related Environmental Monitoring, Federal Environment Agency, UBA, Corrensplatz 1, 14195 Berlin, Germany.
Int J Hyg Environ Health. 2011 Jun;214(3):231-8. doi: 10.1016/j.ijheh.2010.11.004. Epub 2010 Dec 17.
A summary of a critical review by a working group of the German Federal Environment Agency and the German Federal Institute for Risk Assessment on the carcinogenic potential of nanomaterials is presented. After a critical review of the available data, we conclude that the potential carcinogenic risk of nanomaterials can currently be assessed only on a case-by-case basis. There is certain evidence that different forms of CNTs (carbon nanotubes) and nanoscale TiO(2) particles may induce tumours in sensitive animal models. It is assumed that the mode of action of the inhalation toxicity of asbestos-like fibres and of inhalable fractions of biopersistent fine dusts of low toxicity (nano-TiO(2)) is linked to chronic inflammatory processes. Existing epidemiological studies on carcinogenicity for these manufactured nanomaterials are not sufficiently conclusive. Generally speaking, the database is not adequate for an assessment of the carcinogenic potential of nanomaterials. Whereas a number of studies provide evidence of a nano-specific potential to induce tumours, other studies did not. This is possibly due to insufficient characterisation of the test material, difference in the experimental design, the use of different animal models and species and/or differences in dosimetry (both with regard to the appropriate dose metric and the estimated effective dose quantities). An assessment of the carcinogenic potential and its relevance for humans are currently fraught with uncertainty. Furthermore, the nano-specificity of the carcinogenic effects observed cannot be conclusively evaluated. Specific carcinogenic effects of nanomaterials may be both quantitative and qualitative. In quantitative terms, the carcinogenic effects of nanoparticles are thought to be simply more pronounced compared to the corresponding bulk material (due, for example, to the considerably larger surface area and higher number of particles relative to the mass concentration). On the other hand, certain nano-properties such as small size, shape and reactivity, retention time and distribution in the body after overcoming biological barriers, as well as subcellular and molecular interactions may play a role in determining the toxicity in qualitative terms, i.e. the carcinogenic potential of the nanomaterial and the non-nanoscale comparison substance may be fundamentally different. All of these factors leave no doubt about the fact that there is a great need for research in this area and that new standardised test methods need to be developed or existing ones adapted at the very least to achieve valid answers regarding the carcinogenic potential of nanomaterials. Global production of nanomaterials is set to increase in the years to come, and new materials with new properties will be developed, so that greater human exposure to them must be anticipated. No reliable conclusions can currently be drawn about exposure to nanoparticles and their release from products. Firstly, there are substantial deficits in information about the processing of nanomaterials in products and preparations. Secondly, there are only a small number of studies on nanoparticle release, and reliable techniques for measuring and monitoring nanomaterials in different environmental media are still being developed which is both complex and costly. Despite the uncertainties, the findings to date on the carcinogenic potential of nanomaterials must be taken seriously, and precautionary measures to minimise exposure should go hand in hand with the development of a comprehensive and conclusive toxicological methodology and testing procedure for nanostructured materials that includes all possible exposure routes. With regard to possible legal classification of nanomaterials and the transferability of classifications of their non-nanomaterial counterparts, we believe it is necessary to have separate procedures for nano and non-nano forms. Furthermore, criteria for evaluating nano-specific carcinogenic properties should be constantly updated and adapted to the state of knowledge. There is a need here for amendments to be made to EU legislation, as currently nanoforms do not represent a separate category of substance in their own right.
一份由德国联邦环境署和德国联邦风险评估研究所工作组对纳米材料致癌潜力的批判性评论总结如下。在对现有数据进行批判性审查后,我们得出结论,目前只能对个案进行纳米材料潜在致癌风险的评估。有一定的证据表明,不同形式的 CNT(碳纳米管)和纳米级 TiO2颗粒可能会在敏感的动物模型中引起肿瘤。据推测,类似石棉纤维的吸入毒性和低毒性可吸入部分(纳米 TiO2)的生物持久性细粉尘的作用模式与慢性炎症过程有关。这些制造纳米材料的现有致癌性流行病学研究没有足够的结论。一般来说,数据库不足以评估纳米材料的致癌潜力。虽然一些研究提供了纳米材料具有潜在致癌性的证据,但其他研究则没有。这可能是由于对测试材料的特征描述不足、实验设计的差异、使用不同的动物模型和物种以及/或剂量学的差异(包括适当的剂量指标和估计的有效剂量数量)。目前,对纳米材料致癌潜力及其对人类的相关性的评估充满了不确定性。此外,观察到的致癌作用的纳米特异性也不能得出明确的结论。纳米材料的特定致癌作用可能在数量上和质量上都有表现。在数量上,纳米颗粒的致癌作用被认为比相应的体材料更明显(例如,由于与质量浓度相比,纳米颗粒的表面积和颗粒数要大得多)。另一方面,某些纳米特性,如小尺寸、形状和反应性、在克服生物屏障后在体内的保留时间和分布,以及亚细胞和分子相互作用,可能在定性上决定毒性,即纳米材料的致癌潜力和非纳米尺度比较物质可能在根本上不同。所有这些因素都毫无疑问地表明,在这一领域需要进行大量的研究,并且至少需要开发新的标准化测试方法或对现有方法进行调整,以获得关于纳米材料致癌潜力的有效答案。未来几年,全球纳米材料的产量预计将增加,并且将开发具有新特性的新材料,因此预计人类将更多地接触到这些材料。目前,关于纳米颗粒的暴露及其从产品中的释放,还不能得出可靠的结论。首先,关于纳米材料在产品和制剂中的加工的信息存在很大的不足。其次,关于纳米颗粒释放的研究很少,用于测量和监测不同环境介质中纳米材料的可靠技术仍在开发之中,这既复杂又昂贵。尽管存在不确定性,但迄今为止关于纳米材料致癌潜力的发现必须认真对待,应同时采取预防措施,将暴露量降至最低,并同时制定全面和明确的毒理学方法和测试程序,用于对包括所有可能暴露途径的纳米结构材料进行测试。关于纳米材料的可能法律分类和其非纳米材料对应物的分类的可转移性,我们认为有必要为纳米和非纳米形式分别制定程序。此外,评估纳米特异性致癌特性的标准应不断更新,并适应知识状态。在这里,需要对欧盟法规进行修订,因为目前纳米形式本身并不是一种单独的物质类别。
Int J Hyg Environ Health. 2010-12-17
Arch Toxicol. 2012-3-15
Kokuritsu Iyakuhin Shokuhin Eisei Kenkyusho Hokoku. 2009
Arch Toxicol. 2012-4-25
Inhal Toxicol. 2009-7
J Toxicol Environ Health A. 2021-6-3
J Dent Res Dent Clin Dent Prospects. 2019
Medicines (Basel). 2019-3-14
Toxicol Res (Camb). 2018-2-1
Arch Toxicol. 2017-12-22