Elsevier

NeuroToxicology

Volume 84, May 2021, Pages 155-171
NeuroToxicology

Evaluation of the neurotoxic effects of engineered nanomaterials in C57BL/6J mice in 28-day oral exposure studies

https://doi.org/10.1016/j.neuro.2021.03.005Get rights and content

Highlights

  • 28-day neurotoxicity study in mice with foodborne TiO2 and Ag nanomaterial.

  • Absence of neuroinflammation, changes in spontaneous alternation and anxiety-like behavior.

  • Motor function changes in female mice post 28-days exposure to silver nanomaterials.

  • Increased tyrosine kinase activity in cortex of silver nanomaterial exposed female mice.

  • Persistent accumulation of silver in mouse brain up to 4 weeks post-exposure.

Abstract

In recent years, concerns have emerged about the potential neurotoxic effects of engineered nanomaterials (NMs). Titanium dioxide and silver are among the most widely used types of metallic NMs. We have investigated the effects of these NMs on behaviour and neuropathology in male and female C57BL/6J mice following 28-day oral exposure with or without a 14-day post-exposure recovery. The mice were fed ad libitum with food pellets dosed with 10 mg/g TiO2, 2 mg/g polyvinylpyrrolidone-coated Ag or control pellets. Behaviour was evaluated by X-maze, open field, string suspension and rotarod tests. Histological alterations were analysed by immunohistochemistry and brain tissue homogenates were investigated for markers of oxidative stress, inflammation and blood-brain barrier disruption. Effects of the NMs on tyrosine and serine/threonine protein kinase activity in mouse brains were investigated by measuring kinase activity on peptide microarrays.

Markers of inflammation, oxidative stress and blood-brain barrier integrity were not significantly affected in the male and female mice following exposure to Ag or TiO2. Both types of NMs also revealed no consistent significant treatment-related effects on anxiety and cognition. However, in the Ag NM exposed mice altered motor performance effects were observed by the rotarod test that differed between sexes. At 1-week post-exposure, a diminished performance in this test was observed exclusively in the female animals. Cortex tissues of female mice also showed a pronounced increase in tyrosine kinase activity following 28 days oral exposure to Ag NM. A subsequent Inductively Coupled Plasma - Mass Spectrometry (ICP-MS) based toxicokinetic study in female mice revealed a rapid and persistent accumulation of Ag in various internal organs including liver, kidney, spleen and the brain up to 4 weeks post-exposure. In conclusion, our study demonstrated that subacute exposure to foodborne TiO2 and Ag NMs does not cause substantial neuropathological changes in mice. However, the toxicokinetic and specific toxicodynamic findings indicate that long-term exposures to Ag NM can cause neurotoxicity, possibly in a sex-dependent manner.

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.

References (102)

  • I.C. Chen et al.

    ’Influence of silver and titanium dioxide nanoparticles on in vitro blood-brain barrier permeability’

    Environ. Toxicol. Pharmacol.

    (2016)
  • B. Dabrowska-Bouta et al.

    ’Ultrastructural and biochemical features of cerebral microvessels of adult rat subjected to a low dose of silver nanoparticles’

    Toxicology

    (2018)
  • Sylvie Gaillet et al.

    ’SIlver nanoparticles: their potential toxic effects after oral exposure and underlying mechanisms – a review’

    Food Chem. Toxicol.

    (2015)
  • T. Garcia et al.

    ’Oral subchronic exposure to silver nanoparticles in rats’

    Food Chem. Toxicol.

    (2016)
  • Niels Hadrup et al.

    ’Oral toxicity of silver ions, silver nanoparticles and colloidal silver – a review’

    Regul. Toxicol. Pharmacol.

    (2014)
  • Niels Hadrup et al.

    ’The similar neurotoxic effects of nanoparticulate and ionic silver in vivo and in vitro’

    NeuroToxicology

    (2012)
  • Harm J. Heusinkveld et al.

    ’NEurodegenerative and neurological disorders by small inhaled particles’

    NeuroToxicology

    (2016)
  • R. Hu et al.

    ’NEurotoxicological effects and the impairment of spatial recognition memory in mice caused by exposure to TiO2 nanoparticles’

    Biomaterials

    (2010)
  • Melinda E. Lull et al.

    ’MIcroglial activation and chronic neurodegeneration’

    Neurotherapeutics

    (2010)
  • J.F. MacDonald et al.

    ’L-Aspartic acid induces a region of negative slope conductance in the current-voltage relationship of cultured spinal cord neurons’

    Brain Res.

    (1982)
  • E. McGillicuddy et al.

    ’SIlver nanoparticles in the environment: sources, detection and ecotoxicology’

    Sci. Total Environ.

    (2017)
  • Jaime Miquel et al.

    ’A simple technique for evaluation of vitality loss in aging mice, by testing their muscular coordination and vigor’

    Exp. Gerontol.

    (1978)
  • Mark A. Munger et al.

    ’In vivo human time-exposure study of orally dosed commercial silver nanoparticles’

    Nanomedicine

    (2014)
  • E.J. Park et al.

    ’RePeated-dose toxicity and inflammatory responses in mice by oral administration of silver nanoparticles’

    Environ. Toxicol. Pharmacol.

    (2010)
  • J. Skalska et al.

    ’SYnaptic degeneration in rat brain after prolonged oral exposure to silver nanoparticles’

    NeuroToxicology

    (2015)
  • J. Skalska et al.

    ’Oxidative stress in rat brain but not in liver following oral administration of a low dose of nanoparticulate silver’

    Food Chem. Toxicol.

    (2016)
  • M. Valko et al.

    ’Free radicals and antioxidants in normal physiological functions and human disease’

    Int. J. Biochem. Cell Biol.

    (2007)
  • Tina Wahle et al.

    ’Evaluation of neurological effects of cerium dioxide nanoparticles doped with different amounts of zirconium following inhalation exposure in mouse models of Alzheimer’s and vascular disease’

    Neurochem. Int.

    (2020)
  • Jiangxue Wang et al.

    ’Acute toxicity and biodistribution of different sized titanium dioxide particles in mice after oral administration’

    Toxicol. Lett.

    (2007)
  • Additives et al.

    Scientific opinion on the re-evaluation of silver (E 174) as food additive’

    Efsa J.

    (2016)
  • Henriette M.C. Azeredo et al.

    ’Nanostructured antimicrobials in food packaging—recent advances’

    Biotechnol. J.

    (2019)
  • Yoav Benjamini et al.

    ’Controlling the false discovery rate: a practical and powerful approach to multiple testing’

    J. R. Stat. Soc. Ser. B

    (1995)
  • Mary D. Boudreau et al.

    ’Differential effects of silver nanoparticles and silver ions on tissue accumulation, distribution, and toxicity in the sprague dawley rat following daily oral gavage administration for 13 weeks’

    Toxicol. Sci.

    (2016)
  • William K. Boyes et al.

    Neurotoxicology of Nanomaterials’

    Chem. Res. Toxicol.

    (2020)
  • Walter Brand et al.

    ’Possible effects of titanium dioxide particles on human liver, intestinal tissue, spleen and kidney after oral exposure’

    Nanotoxicology

    (2020)
  • Shana J. Cameron et al.

    ’A current overview of the biological and cellular effects of nanosilver’

    Int. J. Mol. Sci.

    (2018)
  • C.S. Chirumamilla et al.

    ’Profiling activity of cellular kinases in migrating T-Cells’

    Methods Mol. Biol.

    (2019)
  • Wan-Seob Cho et al.

    ’Comparative absorption, distribution, and excretion of titanium dioxide and zinc oxide nanoparticles after repeated oral administration’

    Part. Fibre Toxicol.

    (2013)
  • A.S. Dhillon et al.

    ’MAP kinase signalling pathways in cancer’

    Oncogene

    (2007)
  • C. Disdier et al.

    ’Tissue biodistribution of intravenously administrated titanium dioxide nanoparticles revealed blood-brain barrier clearance and brain inflammation in rat’

    Part. Fibre Toxicol.

    (2015)
  • Sameh Eid et al.

    ’KinMap: a web-based tool for interactive navigation through human kinome data’

    BMC Bioinformatics

    (2017)
  • Eric Fabian et al.

    ’Tissue distribution and toxicity of intravenously administered titanium dioxide nanoparticles in rats’

    Arch. Toxicol.

    (2008)
  • FAO/WHO

    ’FAO/WHO Expert Meeting on the Application of Nanotechnologies in the Food and Agriculture Sectors: Potential Food Safety Implications: Meeting Report. Rome.

    (2010)
  • FDA
  • X. Feng et al.

    ’Central nervous system toxicity of metallic nanoparticles’

    Int. J. Nanomedicine

    (2015)
  • Emily Foran et al.

    ’Glutamate transporters and the excitotoxic path to motor neuron degeneration in amyotrophic lateral sclerosis’

    Antioxid. Redox Signal.

    (2009)
  • Swati Gajbhiye et al.

    ’SIlver nanoparticles in cosmetics’

    J. Cosmet. Dermatol. Sci. Appl.

    (2016)
  • H. Gao et al.

    ’Introduction and overview

  • Liesbeth Geraets et al.

    ‘Tissue distribution and elimination after oral and intravenous administration of different titanium dioxide nanoparticles in rats’

    Part. Fibre Toxicol.

    (2014)
  • Shahab Ghaderi et al.

    ’Induced adverse effects of prenatal exposure to silver nanoparticles on neurobehavioral development of offspring of mice’

    J. Toxicol. Sci.

    (2015)
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    Current address: State Office for Consumer Protection Saxony-Anhalt, Stendal, Germany.

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