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VU Research Portal Ecotoxicological assessment of ZnO nanoparticles to Folsomia candida Waalewijn-Kool, P.L. 2013 document version Publisher's PDF, also known as Version of record Link to publication in VU Research Portal citation for published version (APA) Waalewijn-Kool, P. L. (2013). Ecotoxicological assessment of ZnO nanoparticles to Folsomia candida. Off-Page, www.offpage.nl. General rights Copyright and moral rights for the publications made accessible in the public portal are retained by the authors and/or other copyright owners and it is a condition of accessing publications that users recognise and abide by the legal requirements associated with these rights. • Users may download and print one copy of any publication from the public portal for the purpose of private study or research. • You may not further distribute the material or use it for any profit-making activity or commercial gain • You may freely distribute the URL identifying the publication in the public portal ? Take down policy If you believe that this document breaches copyright please contact us providing details, and we will remove access to the work immediately and investigate your claim. E-mail address: [email protected] Download date: 04. Oct. 2021 Ecotoxicological assessment of ZnO nanoparticles to This Ph.D. thesis focuses on the ecotoxicity and bioavailability of ZnO nanoparticles (ZnO-NP) for a Ecotoxicological assessment of ZnO soil-dwelling organism, the springtail Folsomia nanoparticles to Folsomia candida candida. Different fate and effect studies were performed in natural soils to unravel the contribution of particulate and dissolved Zn to ZnO-NP toxicity. This study shows that the release of toxic Zn2+ ions P.L. Waalewijn-Kool from ZnO-NP continues for at least one year, but that this does not lead to increased toxicity. This research suggests that ZnO-NP can be evaluated using the current risk assessment of Zn. The studies performed during this Ph.D. project were part of the European project NanoFATE (Nanoparticle Fate Assessment and Toxicity in the Environment). Folsomia candida P.L. Waalewijn-Kool P.L. Ecotoxicological assessment of ZnO nanoparticles to Folsomia candida Pauline Lydia Waalewijn-Kool This research was conducted in the context of NanoFATE, Collaborative Project CP-FP 247739 (2010-2014) under the 7th Framework Programme of the European Commission (FP7-NMP-ENV-2009, Theme 4). Thesis 2013-06 of the Department of Ecolocial Science, VU University Amsterdam, The Netherlands Layout and printing: Off-Page, www.offpage.nl ISBN: 978-94-6182-324-3 VRIJE UNIVERSITEIT Ecotoxicological assessment of ZnO nanoparticles to Folsomia candida ACADEMISCH PROEFSCHRIFT ter verkrijging van de graad Doctor aan de Vrije Universiteit Amsterdam, op gezag van de rector magnificus prof.dr. F.A. van der Duyn Schouten in het openbaar te verdedigen ten overstaan van de promotiecommissie van de Faculteit der Aard- en Levenswetenschappen op donderdag 24 oktober 2013 om 11.45 uur in de aula van de universiteit, De Boelelaan 1105 door Pauline Lydia Waalewijn-Kool geboren te Leiderdorp promotor: prof.dr. N.M. van Straalen copromotor: dr.ir. C.A.M. van Gestel “Ik heb u tot een keurmeester van metalen gemaakt, zodat u het erts kunt testen en de waarde ervan kunt bepalen.” Jeremia 6:27. Het Boek, oktober 2009 Table of contents Chapter 1 General introduction 9 Chapter 2 Effect of different spiking procedures on the distribution 25 and toxicity of ZnO nanoparticles in soil Chapter 3 Chronic toxicity of ZnO nanoparticles, non-nano ZnO and 39 ZnCl2 to Folsomia candida (Collembola) in relation to bioavailability in soil Supporting Information 52 Chapter 4 Sorption, dissolution and pH determine the long-term 57 equilibration and toxicity of coated and uncoated ZnO nanoparticles in soil Supporting Information 69 Chapter 5 The effect of pH on the toxicity of ZnO nanoparticles to 84 Folsomia candida in amended field soil Supporting Information 98 Chapter 6 Effect of soil properties on the toxicity of ZnO nanoparticles 107 to Folsomia candida in a comparison of four natural soils Supporting Information 120 Chapter 7 Summary and discussion 129 Bibliography 145 Appendix I Summary of ecotoxicity studies with ZnO nanoparticles 156 (ZnO-NP) and terrestrial invertebrates Appendix II Letter to the Editor. Metal-based nanoparticles in soil: 158 New research themes should not ignore old rules and theories Samenvatting 163 Acknowledgements 167 Curriculum vitae 169 SENSE Certificate 171 1General introduction General introduction 1 1Scope Nano is a prefix meaning extremely small. When quantifiable, it translates to one- billionth. The term “nano-technology” was first used by Norio Taniguchi in 1974 and refers to the engineering of functional systems at the molecular scale (Maynard, 2006). Nowadays different types of zinc oxide nanoparticles (ZnO-NP) can be purchased on the commercial market with the potential of being released in the environment (Gottschalk and Nowack, 2011). Although the size-dependent properties make engineered nanoparticles (ENPs) desirable for many applications, their release into the environment and implications for the environmental fate and effects need to be investigated (Klaine et al., 2008). This thesis focuses on how ZnO-NP reacts in natural soils and how toxic these particles are for a soil dwelling organism, Folsomia candida. In this Chapter I introduce ZnO-NP as one of the most widely used ENPs and their route into the soil environment. Then, I describe the fate processes that tend to occur when ZnO-NP are in the soil and how these processes relate to soil properties. An overview of available terrestrial studies is shown, indicating adverse effects of ZnO-NP to soil organisms. And an outline of the thesis is given in which the investigated aspects of the fate and effects assessment of ZnO-NP are addressed. 2 Engineered nanoparticles ENPs exhibit novel properties with specific and improved functionality and increased efficiency (Navarro et al., 2008). The physico-chemical properties of ENPs are attributable to their small size (surface area and size distribution), chemical composition (purity, crystallinity, electronic properties), surface structure (surface reactivity, surface groups, inorganic or organic coatings), solubility, shape, and aggregation (Nel et al., 2006; Hassellöv et al., 2008). The surface area-to-volume ratio is a function of particle size, with smaller particles having a larger surface area per weight than larger particles (Bottero et al., 2011). Their higher surface to volume ratio makes ENPs potentially more reactive than larger particles. Approximately 35-40% of the atoms are localized at the surface of a 10 nm nanoparticle compared to less than 20% for a particle larger than 30 nm (Auffan et al., 2009). ENPs are used in a large variety of industrial and consumer products, such as medical devices, pharmaceuticals, cosmetics, electronics, textiles, food packaging, fuel catalysts, biosensors and for environmental remediation. The use of ENPs has grown dramatically in the last decade and will continue growing in the coming years (Aitken et al., 2006; Royal Society, 2004). The commercially useful properties of ENPs have resulted in a large range of different ENPs. They can be classified based on their chemical composition into carbon-containing (organic) and metal-based (inorganic) 11 Chapter 1 ENPs (Nowack et al., 2007; Peralta-Videa et al., 2011). Inorganic ENPs include metal and metal oxide nanoparticles such as silver (Ag), which are widely incorporated into products for their antibacterial and antifungal properties; titanium oxide (TiO2) and zinc oxide (ZnO), which are used in sunscreens for their ultraviolet (UV) absorbance and reflecting capability; and cerium oxide (CeO2), which is used in fuel additives as a catalyst. Mixtures of different phases are also manufactured (e.g. cadmium selenide). ENPs can be produced by a huge range of procedures which can be grouped into top-down and bottom-up strategies (Ju-Nam and Lead, 2008). Top-down approaches are defined as those by which ENPs are directly generated from bulk materials using physical methods such as milling, attrition or repeated quenching. Bottom-up strategies involve molecular components as starting materials linked with chemical reactions, nucleation and growth processes (Christian et al., 2008). ENPs can be produced with different shapes or structures; they can be spherical, tubular or irregularly shaped and can have a functionalized surface or a coating (Nowack et al., 2007). ENPs are defined as manufactured particles with sizes smaller than 100 nm in one or more dimensions. The cut-off value of 100 nm is considered the working definition of the International Organization for Standardization (ISO, 2008) and used by many researchers working with ENPs nowadays (e.g. Handy et al., 2008; Heinlaan et al., 2008; Unrine et al., 2010). As ENPs rarely have one size after release into the environment, it is more realistic to consider ENPs with a distribution of particle sizes around the nanoscale (Handy et al., 2008). The European Union recommends considering particle size distributions in the definition of ENPs instead of one particle size only. This means that when 50% of the total number of particles in a certain material has one or more dimensions smaller than 100 nm, all material is considered as nanomaterial. The definition of the European Union for nanomaterials reads: “Nanomaterial means a natural, incidental or manufactured material containing particles,