Evaluation of the neurotoxic effects of engineered nanomaterials in C57BL/6J mice in 28-day oral exposure studies
Introduction
The widespread use of engineered metallic nanomaterials (NMs) in various consumer products has led to a growing concern about their adverse effects on human health. Depending on their physico-chemical properties (e.g. size, agglomeration, surface reactivity) and their route of exposure (e.g. inhalation, ingestion, dermal exposure, intravenous application), NMs may be absorbed into the body and distributed to different secondary target organs and tissues (Oberdörster et al., 2005). In recent years, there has been increasing interest in the investigation of the central nervous system (CNS) as target organ for NMs (Boyes et al., 2012; Boyes and van Thriel, 2020). Initial awareness of the potential adverse effects of nanosize particles on the CNS came with a study that demonstrated translocation of ultrafine particles into the brains of rats upon short-term inhalation exposure (Oberdörster et al., 2004). Since then, several rodent inhalation studies have provided support for the effects of nanoparticles on the brain and, thereby, revealed a mechanistic link to epidemiological studies that show an association between exposure to ambient air pollution particles and neurological diseases (reviewed by (Heusinkveld et al., 2016)). While inhalation represents the primary exposure route for ambient (nanosize) particles as well as for many bulk-manufactured NMs in occupational settings, oral exposure to NMs has also become a topic of increasing investigation. Concerns about the adverse health effects of ingested NMs, including neurotoxicity, have emerged with the growing number of applications in nanomedicine and, in particular, the food sector where NMs are used e.g. as food additives or in food packaging (Bouwmeester et al., 2009; Sohal et al., 2018).
For inhalation exposure, the translocation of NMs via the olfactory nerve into the brain has emerged as an important exposure route (Heusinkveld et al., 2016; Oberdörster et al., 2005). However, for ingested NMs, brain targeting of these particulate entities or their dissolved compounds requires the translocation from the gastrointestinal tract into the circulation and subsequent passage of the blood-brain barrier (BBB). Absorption from the gastrointestinal tract has been shown for various NMs, including silver (Ag) and titanium dioxide (TiO2) (Geraets et al., 2014; Kreyling et al., 2017; Lee et al., 2019; Wang et al., 2007; Boudreau et al., 2016; Loeschner et al., 2011; van der Zande et al., 2012). Furthermore, crossing of the BBB and accumulation into the CNS has been suggested for Ag and TiO2 in several studies that applied intravenous or oral administration (Kreyling et al., 2017; Lee et al., 2019; Fabian et al., 2008; Disdier et al., 2015; Loeschner et al., 2011; Recordati et al., 2015; van der Zande et al., 2012). Ag and TiO2 have also been reported to disrupt the BBB integrity (Trickler et al., 2010; Brun et al., 2012; Xu et al., 2015).
The main mechanisms whereby NMs can cause neurotoxicity in the CNS are thought to be through the induction of oxidative stress and inflammation (Feng et al., 2015; Song et al., 2016; Boyes and van Thriel, 2020). Because of its high content of polyunsaturated fatty acids and low concentrations of antioxidants and antioxidant enzymes, the brain is more sensitive to oxidative stress than other tissues (Valko et al., 2007; Oberdörster et al., 2009; Islam, 2017). Indeed, increased levels of the lipid peroxidation marker malondialdehyde (MDA) and changes in the glutathione antioxidant defense system have been shown in the brain but not in the liver of rats after repeated oral gavage application of Ag NM (Skalska et al., 2016).
Despite the increasing number of neurotoxicological studies on metallic NMs, their role in neuroinflammation has not yet been well understood. It is suggested to result from their ability to activate microglia and astrocytes. Activation of these glial cell types results in secretion of mediators triggering neuronal repair or the release of proinflammatory cytokines and reactive oxygen species, resulting in neuroinflammation (Mayer et al., 2013). Increased expression of the glial fibrillary acidic protein (GFAP), which is expressed in astrocytes (Sofroniew and Vinters., 2010), and ionized calcium-binding adapter molecule 1 (IBA-1), which is expressed upon activation of microglia (Kovacs, 2017) are therefore recognised as important markers of neuroinflammation. In response to exposure to NMs, microglia cells have been shown to enhance the release of proinflammatory cytokines, whereas astrocytes prefer to increase the production of anti-inflammatory factors (Wu and Tang., 2017). The acute innate pro-inflammatory cytokines tumour necrosis factor α (TNF-α), interleukin 1β (IL-1β) and IL-6 are all regulated by mitogen activated protein kinase (MAPK) signalling pathway (Wu and Tang, 2017). These serine-threonine protein kinases regulate cellular activities including proliferation, differentiation, apoptosis or survival and inflammation (Kim and Choi, 2015). Tyrosine kinases represent another type of protein kinase that regulate the majority of cellular pathways as well. They can be subdivided into the receptor tyrosine kinases which have extra-cellular ligand-binding domains and the cytoplasmic (i.e. nonreceptor) tyrosine kinases (Shah et al., 2018). Altered activities of protein kinase signalling pathways have been implicated in the pathology of diverse human diseases including cancer and neurodegeneration (Dhillon et al., 2007; Rosenberger et al., 2016).
In this study, we investigated the potential neurotoxic effects of two different types of NMs in male and female C57BL/6J mice in a 28-day oral repeated exposure design including a 14-day post-exposure recovery period. We choose TiO2 and Ag since these are widely used metal based NMs in numerous consumer applications and products (Vance et al., 2015; FAO/WHO, 2010). Oral exposure studies with NMs in rodents predominantly have used gavage as the method of their administration. However, while this bolus application procedure ensures a precise dosimetry, it poorly represents the way in which humans may typically be exposed. Accordingly, in our present study, we explored the effects of the TiO2 and Ag NMs by their incorporation into the mouse feed pellets. The aim of our study was to explore the effects of repeated oral exposures to these NMs on neurobehaviour and expression of markers of oxidative stress, inflammation and blood-brain-barrier disruption, with specific evaluation of sex-specificity of treatment-related changes. Effects of the NMs on tyrosine and serine/threonine protein kinases activity were investigated using peptide microarrays.
Section snippets
Nanomaterials
For this study, we used TiO2-P25 (JRC reference nanomaterial NM105) and 0.2% polyvinylpyrrolidone (PVP) coated Ag (Sigma-Aldrich, USA: #576832−5 G, Lot #MKBX3387 V). Scanning electron microscopy (SEM) imaging of the NMs was performed to determine the morphology, size distribution and primary particle size of the specific batch of the NMs that were used in our study. The size distribution of the TiO2 NM displayed a mean size of 26.2 nm ± 10.7 nm and a nearly spherical particle morphology. The
Effects of oral exposure to TiO2 and Ag NMs on body and organ weights
The body weights of the mice were determined prior to the first oral exposure as well as on day 28 and 42 (i.e. on day 14 of the exposure recovery period). Organ weights were determined at sacrifice days 28 and 42. Results are shown in Table 1. As can be seen in the table, there were no obvious treatment related effects on body organ weights in the mice. In the male mice of substudy II (recovery groups), kidney weights/g body weight were lower for the TiO2 fed male mice compared to
Discussion
Contrasting data have been reported in literature regarding the neurotoxicity of NMs following oral exposure. In this study we examined the effects of two widely applied metallic NMs, i.e. TiO2 and Ag in male and female C57BL/6J mice in a 28-day oral exposure study with or without a 14-day post-exposure recovery period. TiO2 and Ag are used in various consumer applications (Hadrup and Lam, 2014; Munger et al., 2014; Shakeel et al., 2016; Gajbhiye and Sakharwade, 2016; Rai and Shegokar, 2017).
Conclusions
We investigated the neurotoxicity of TiO2 and Ag NMs, applied in food pellets, in male and female C57BL/6 J mice in a 28-day oral exposure study with or without a 14-day post-exposure recovery period. No major neuropathological changes regarding neuroinflammation in biochemical and immunohistochemical analyses could be observed and behavioural changes in anxiety and cognition were absent. However, in the Ag NM exposed mice motor performance effects were observed by the rotarod test that
Funding/Support
This article presents independent research funded by the German Federal Ministry of Education and Research (BMBF/InnoSysTox-Verbund, Grant number: FKZ 031L0020A).
Role of the Funder/Sponsor
The funders had no role in the design and implementation of the study; management, analysis, and interpretation of the data; preparation, review, or approval of the manuscript; and decision to submit the manuscript for publication.
Disclaimer
The views expressed are those of the authors and not necessarily those of the BMBF/InnoSysTox-Verbund.
CRediT authorship contribution statement
Adriana Sofranko: Conceptualization, Methodology, Investigation, Validation, Formal analysis, Data curation, Writing - original draft, Writing - review & editing, Visualization. Tina Wahle: Conceptualization, Methodology, Investigation, Data curation. Harm J. Heusinkveld: Conceptualization, Methodology, Funding acquisition. Burkhard Stahlmecke: Conceptualization, Methodology, Investigation, Data curation, Visualization, Funding acquisition. Michail Dronov: Methodology, Investigation, Data
Declaration of Competing Interest
The authors declare that they have no competing interests.
Acknowledgements
The work leading to these results has received funding from the German Federal Ministry of Education and Research (BMBF/InnoSysTox-Verbund, Grant number: FKZ 031L0020A). We thank Isabelle Masson, Gabriele Wick and Petra Gross (IUF) for technical support. We also thank Uwe Karst (Institute of Inorganic and Analytical Chemistry, University of Münster) as well as Daniel Breitenstein and Birgit Hagenhoff (both Tascon GmbH) for equipment support and advice on the ToF-SIMS and LA-ICP-MS analyses.
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Current address: State Office for Consumer Protection Saxony-Anhalt, Stendal, Germany.