Federal Institute for Occupational Safety and Health, 44149, Dortmund, Germany,
Arch Toxicol. 2014 Dec;88(12):2191-211. doi: 10.1007/s00204-014-1383-7. Epub 2014 Oct 19.
Nanotechnology offers enormous potential for technological progress. Fortunately, early and intensive efforts have been invested in investigating toxicology and safety aspects of this new technology. However, despite there being more than 6,000 publications on nanotoxicology, some key questions still have to be answered and paradigms need to be challenged. Here, we present a view on the field of nanotoxicology to stimulate the discussion on major knowledge gaps and the critical appraisal of concepts or dogma. First, in the ongoing debate as to whether nanoparticles may harbour a specific toxicity due to their size, we support the view that there is at present no evidence of 'nanospecific' mechanisms of action; no step-change in hazard was observed so far for particles below 100 nm in one dimension. Therefore, it seems unjustified to consider all consumer products containing nanoparticles a priori as hazardous. Second, there is no evidence so far that fundamentally different biokinetics of nanoparticles would trigger toxicity. However, data are sparse whether nanoparticles may accumulate to an extent high enough to cause chronic adverse effects. To facilitate hazard assessment, we propose to group nanomaterials into three categories according to the route of exposure and mode of action, respectively: Category 1 comprises nanomaterials for which toxicity is mediated by the specific chemical properties of its components, such as released ions or functional groups on the surface. Nanomaterials belonging to this category have to be evaluated on a case-by-case basis, depending on their chemical identity. Category 2 focuses on rigid biopersistent respirable fibrous nanomaterials with a specific geometry and high aspect ratio (so-called WHO fibres). For these fibres, hazard assessment can be based on the experiences with asbestos. Category 3 focuses on respirable granular biodurable particles (GBP) which, after inhalation, may cause inflammation and secondary mutagenicity that may finally lead to lung cancer. After intravenous, oral or dermal exposure, nanoscaled GBPs investigated apparently did not show 'nanospecific' effects so far. Hazard assessment of GBPs may be based on the knowledge available for granular particles. In conclusion, we believe the proposed categorization system will facilitate future hazard assessments.
纳米技术为技术进步带来了巨大的潜力。幸运的是,人们已经投入了大量的早期和密集的努力来研究这项新技术的毒理学和安全性方面。然而,尽管已经有超过 6000 篇关于纳米毒理学的出版物,但仍有一些关键问题需要回答,一些范式需要受到挑战。在这里,我们提出了对纳米毒理学领域的看法,以激发对主要知识空白的讨论,并对概念或教条进行批判性评估。首先,在关于纳米颗粒是否因其尺寸而具有特定毒性的持续争论中,我们支持这样一种观点,即目前没有证据表明存在“纳米特异性”作用机制;迄今为止,一维尺寸小于 100nm 的颗粒没有观察到危害的明显变化。因此,没有理由预先认为所有含有纳米颗粒的消费品都是危险的。其次,目前还没有证据表明纳米颗粒的生物动力学有根本的不同会引发毒性。然而,关于纳米颗粒是否可能积累到足以引起慢性不良反应的程度,数据仍然很少。为了便于危害评估,我们建议根据暴露途径和作用模式将纳米材料分为三类:第 1 类包括纳米材料,其毒性是由其成分的特定化学性质介导的,例如表面释放的离子或官能团。属于这一类的纳米材料必须根据其化学特性进行个案评估。第 2 类重点是具有特定几何形状和高纵横比的刚性持久可呼吸纤维状纳米材料(所谓的世卫组织纤维)。对于这些纤维,可以根据对石棉的经验进行危害评估。第 3 类重点是可呼吸的颗粒状生物可降解颗粒(GBP),吸入后可能引起炎症和继发突变性,最终导致肺癌。在静脉、口服或皮肤暴露后,迄今为止研究的纳米级 GBP 似乎没有表现出“纳米特异性”效应。GBP 的危害评估可以基于现有的颗粒状物质的知识。总之,我们相信所提出的分类系统将有助于未来的危害评估。