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Timing, hosts and locations of (grouped) events of NanoImpactNet

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4 Description <strong>of</strong> the work performed since<br />

the beginning <strong>of</strong> the project <strong>and</strong> the main<br />

results achieved<br />

While work has begun on all nine <strong>of</strong> the main NanoFATE S&T<br />

objectives (see above), obviously some are targeted for early<br />

delivery (i.e. Obj. 1 <strong>and</strong> 2) while full delivery for the others will<br />

not come till the end <strong>of</strong> the project. For more details than the<br />

summary below <strong>and</strong> for access to completed public deliverables,<br />

updates <strong>and</strong> subscription to newsletters, please use the website<br />

www.nan<strong>of</strong>ate.eu .<br />

The working objectives addressed in the first 18 months <strong>of</strong><br />

NanoFATE to ensure timely progress towards the overall<br />

objectives can be summarised as follows:<br />

I. Source, produce <strong>and</strong> fully characterise the<br />

commercial ENPs <strong>and</strong> match the tagged version <strong>of</strong><br />

ZnO as closely as possible. (Delivering Main Obj. 1)<br />

II. Establish particle behaviour in the pure ecotox<br />

media to be used <strong>and</strong> at higher than<br />

environmental concentrations (to enable hazard<br />

assessment studies). (Working towards Main Obj.<br />

3, 4 & 5)<br />

III. Establish acute <strong>and</strong> chronic toxicity (to enable<br />

selection <strong>of</strong> relevant doses for the progression<br />

into the work in environmentally relevant media<br />

conditions. (Working towards Main Obj. 5, 6, 7 &<br />

8)<br />

IV. Develop initial simple assumption based fate<br />

models <strong>and</strong> estimate worst case environmental<br />

concentrations (Working towards Main Obj. 2 & 8)<br />

V. Train all staff cross discipline, <strong>and</strong> disseminate our<br />

early findings <strong>and</strong> planned directions to other EU<br />

projects <strong>and</strong> stakeholders (Main Obj. 9)<br />

WP 1. Characterisation <strong>and</strong> tracking <strong>of</strong> ENPs during processes<br />

involved in fate <strong>and</strong> toxicity.<br />

In the first 18 months the major deliverables here related to<br />

provision <strong>of</strong> high quality well characterised particles for the<br />

remaining project partners. A larger than planned range <strong>of</strong><br />

commercial ENPs were characterised <strong>and</strong> assessed so that<br />

supply was consistent <strong>and</strong> without significant batch to batch<br />

variation issues. Consequently the final set <strong>of</strong> NanoFATE<br />

commercial particles are:<br />

• The main ZnO particles are 30nm Nanosun from<br />

micronisers in Australia, with matching tagged ZnO<br />

ENP by IHPP, with some work on BASF z-cote <strong>and</strong> zcote<br />

HP1 ZnO<br />

• Amepox 3-8nm Ag ENP <strong>and</strong> a 50nm Ag NP from<br />

NanoTrade<br />

• CeO 2 will be the Envirox or Antaria fuel additive <strong>and</strong><br />

most likely a polishing agent from Umicore.<br />

WP 2. ENP environmental behaviour <strong>and</strong> fate modelling<br />

Have identified <strong>and</strong> prioritised specific properties that need<br />

principal consideration during the development, adaptation <strong>and</strong><br />

validation <strong>of</strong> environmental fate models for nanoparticles (D2.1).<br />

They have, based on this, developed the initial basic fate models<br />

NanoSafetyCluster - Compendium 2012<br />

(with WP6) <strong>and</strong> supplied the initial worst case environmental<br />

concentration estimates serving to inform decision making <strong>and</strong><br />

exposure design in WP 3 & 4 (M 2.1 <strong>and</strong> D 2.2).<br />

WP 3 ENP Ecotoxicology<br />

Developed improved st<strong>and</strong>ard ecotox exposure protocols,<br />

principally adjusting properties <strong>of</strong> test media, media renewal<br />

frequencies <strong>and</strong> soil <strong>and</strong> food spiking methodologies, to ensure<br />

relevant <strong>and</strong> homogenous presentation <strong>of</strong> nanoparticles during<br />

toxicity testing. Employing these improved protocols most <strong>of</strong><br />

the exposures needed for the hazard assessment has been<br />

completed (except for CeO 2). This information has allowed<br />

progress into the chronic testing phase <strong>and</strong> also some work to<br />

deliver the data for WP4 on bioavailability drivers.<br />

WP 4 ENP bioavailability - relations between soil <strong>and</strong> water<br />

chemistry <strong>and</strong> particle properties<br />

Collected <strong>and</strong> databased all available information from<br />

literature, conferences <strong>and</strong> other projects <strong>and</strong> conducted a<br />

critical review <strong>of</strong> this available data <strong>and</strong> its quality. This<br />

identified which environmental factors have the greatest<br />

proven effect on the bioavailability <strong>and</strong> toxicity <strong>of</strong> nanoparticles<br />

to organisms living in soil <strong>and</strong> water. Based on this initial<br />

bioavailability trials testing for pH, organic matter <strong>and</strong> cation<br />

effects have been designed <strong>and</strong> run within WP3, plus additional<br />

long-term (12 months) exposures addressing ageing have been<br />

set up.<br />

WP 5 ENP toxicokinetics <strong>and</strong> toxicodynamics<br />

The WP5 workshop session in Portugal (Jan 2011) developed a<br />

practical <strong>and</strong> workable sample h<strong>and</strong>ling <strong>and</strong> preservation<br />

system to enable the success <strong>of</strong> NanoFATE tissue banking. A<br />

well thought through tired approach to the tracking <strong>of</strong> ENPs in<br />

tissues was also developed, allowing us to make the most <strong>of</strong> our<br />

technical abilities (<strong>and</strong> tissue samples) by ensuring that the highend<br />

expensive low throughput techniques only to be applied to<br />

samples where we have good evidence ENPs are present.<br />

Samples have been run looking at biological markers <strong>of</strong> ENP <strong>and</strong><br />

dissolved metal effects to develop the knowledge <strong>of</strong> signatures<br />

<strong>of</strong> possible ENP tissue damage. An agreed data structure has<br />

been developed for this systematic data to allow later cross<br />

species comparison, <strong>and</strong> the format has been kept flexible to<br />

enable adaptation to the Cluster database when agreed. A few<br />

samples have been run on the UK synchrotron at Diamond Light<br />

Source to provide a highly characterised test bed for<br />

development <strong>of</strong> other more accessible techniques.<br />

WP 6 Integrated risk assessment<br />

The initial milestone for WP 6 was to assess ENP production <strong>and</strong><br />

product incorporation estimation engaging industry directly<br />

through a survey. With over 560 companies <strong>and</strong> associations<br />

involved in ENP production being contacted this represented an<br />

important attempt to gain intelligence on market size <strong>and</strong><br />

growth for ENPs in Europe. However, a devastating lack <strong>of</strong><br />

industry willingness to interact was suffered, as was the case for<br />

a similar effort by the NanoSustain project. Therefore the report<br />

was based upon a review <strong>of</strong> the peer-reviewed as well as grey<br />

literature (reports from R&D projects, reports to governmental<br />

Compendium <strong>of</strong> Projects in the European NanoSafety Cluster 103

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