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Challenges of Regulation and Risk Assessment of Nanomaterials

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Primary <strong>and</strong> secondary characterization <strong>of</strong> the ENPRA ENP<br />

Jensen K.A. 1 , Bilanikova D. 2 , Brunelli A. 2 , Pojana G. 2 , Birkedal R. 1 , Levin M. 1 , Koponen I.K. 1 ,<br />

K<strong>of</strong>oed-Sørensen V. 1 , Clausen P.A. 1 , Marcomini A. 2 , Jacobsen N.R. 1 , Wallin H. 1<br />

1 National Research Centre for the Working Environment, Copenhagen, Denmark<br />

2 University Ca’ Foscari Venice, Italy<br />

The nanomaterials in ENPRA comprise six materials from the OECD WPMN sponsorship programme<br />

[NM101 (TiO2), NM110 (ZnO), NM111 (silane-coated ZnO), NM300 (dispersed silver particles: Ag),<br />

NM400 (carbon coated multi-walled carbon nanotube) <strong>and</strong> NM402 (multi-walled carbon nanotube)].<br />

Additional four TiO2 samples were selected: A 10 nm- (NRCWE-001) <strong>and</strong> a 100 nm-size rutile TiO2<br />

(NRCWE-004) <strong>of</strong> which a subsample <strong>of</strong> NRCWE-001 was modified to achieve a chemical positive<br />

(NRCWE-002) <strong>and</strong> negative charge (NRCWE-003). All test materials were selected to obtain a<br />

“dynamic range” in physico-chemical properties <strong>and</strong> toxicity.<br />

In this work, we characterize the selected test materials <strong>and</strong> the particle characteristics in the in<br />

batch dispersion <strong>and</strong> in vitro exposure mediums. We have also established a common serum-based<br />

method for particle batch dispersion for the ENPRA toxicity testing. The primary characterization is<br />

important to document the test materials (Figure 1), but the data are also highly warranted as many<br />

<strong>of</strong> the end-points (especially primary size <strong>and</strong> surface area) are thought to play a mechanistic role in<br />

particle toxicity. In addition, we also describe the hydrochemical reactivity (hydroxyl radical<br />

formation capacity <strong>and</strong> redox potential in test mediums) <strong>of</strong> the NMs <strong>and</strong> their emission potential by<br />

rotating drum dustiness testing.<br />

Some <strong>of</strong> the major challenges in the characterization <strong>of</strong> primary physico-chemical characteristics, are<br />

inappropriate methods for bulk characterization <strong>of</strong> CNT, method-dependent results on size<br />

distributions, variation in metal catalyst extraction efficiencies from CNT for ICP elemental analysis,<br />

quantitative analysis <strong>of</strong> unknown organic ENP surface functionalisations, applicability <strong>of</strong> the noncatalyzed<br />

benzoic acid test method for quantification <strong>of</strong> intrinsic hydroxyl radical formation capacity.<br />

Methods <strong>and</strong> results will be discussed in the lecture <strong>and</strong> special focus will be set on the need to<br />

improve our underst<strong>and</strong>ing <strong>of</strong> test item preparation <strong>and</strong> the behavior <strong>and</strong> reactivity <strong>of</strong> NM in both<br />

exposure mediums <strong>and</strong> specific biological compartments.<br />

Figure 1. Overview <strong>of</strong> the main primary physico-chemical<br />

characteristics <strong>and</strong> analytical methods applied in ENPRA. As<br />

indicated by the arrows, several methods can give supporting<br />

information to improve the underst<strong>and</strong>ing <strong>of</strong> the materials.<br />

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