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

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2.9 Project Management (WP9)<br />

This work package covers the management <strong>and</strong> coordination <strong>of</strong><br />

the project. All planned activities will be closely monitored <strong>and</strong> if<br />

necessary, corrections will be performed. The coordinator will be<br />

responsible <strong>of</strong> coordinating the overall running <strong>of</strong> the whole<br />

project <strong>and</strong>, with the help <strong>of</strong> the Project Management Team, will<br />

ensure that all planned activities are pursued.<br />

3 Current status <strong>of</strong> the project<br />

Nanopolytox is a 3-year project which started in May 2010; the<br />

advances on the project for the last 18 months will be described<br />

below.<br />

3.1 Synthesis <strong>and</strong> characterization <strong>of</strong> NM<br />

The main goal <strong>of</strong> WP1 was to synthesize <strong>and</strong> characterize the<br />

nanomaterials to be used for the development <strong>of</strong> the whole<br />

project.<br />

The syntheses <strong>of</strong> the selected nanomaterials (MWCNT, nanoclays<br />

<strong>and</strong> metal oxide nanoparticles) have been carried out following<br />

different methods. MWCNT were synthesized by catalytic chemical<br />

vapor deposition (CCVD) processes at high temperatures obtaining<br />

CNT with high purities. The synthesis <strong>of</strong> MWCNT with different<br />

surface properties (hydrophobic, amphiphatic <strong>and</strong> hydrophilic)<br />

was performed using wet chemistry procedures. The synthesis <strong>of</strong><br />

nanoclays (two types <strong>of</strong> nanoclays with different particle size) was<br />

carried out by a two step wet chemistry procedure: Purification <strong>of</strong><br />

the natural occurring clays <strong>and</strong> subsequent ion exchange reaction<br />

to modify the nanoclays with three different content or structure<br />

<strong>of</strong> quaternary ammonium salts. Furthermore, metal oxide<br />

nanoparticles (SiO 2, TiO 2 <strong>and</strong> ZnO NP) were synthesized by the<br />

flame spray pyrolysis process which relies on the direct<br />

introduction <strong>of</strong> liquid raw materials into a flame. Metal oxide NP<br />

have been functionalized by wet chemistry leading to NP with<br />

different surface properties (hydrophobic, amphiphatic <strong>and</strong><br />

hydrophilic). The physico-chemical characterization <strong>of</strong> all the<br />

nanomaterials synthesized was carried out using the following<br />

analytical techniques: Transmission Electron Microscopy (TEM),<br />

Scanning Electron Microscopy (SEM) analyses <strong>and</strong> X-Ray Scattering<br />

techniques (XRS <strong>and</strong> XRD) <strong>and</strong> to determine the size<br />

crystallography <strong>and</strong> geometry <strong>of</strong> the nanomaterials, Dynamic Light<br />

Scattering (DLS) measurements to determine the hydrodynamic<br />

radius in solution, <strong>and</strong> BET analyses for the porosity <strong>and</strong> surface<br />

area determination. The chemical characterization included<br />

determination <strong>of</strong> the chemical composition <strong>of</strong> nanomaterials, their<br />

surface functionalities <strong>and</strong> their stability using Inductively Coupled<br />

Plasma Mass Spectrometry (ICP-MS), Fourier Transform Infrared<br />

Spectroscopy (FTIR), Ultraviolet-visible Spectroscopy (UV-vis) <strong>and</strong><br />

ζ-potential, respectively. The data collected was included in the<br />

technical card which will be the ID <strong>of</strong> the nanomaterials through all<br />

their life cycle.<br />

3.2 Development <strong>of</strong> polymer nanocomposites<br />

Polymeric matrices have been selected for the studies <strong>of</strong> this<br />

project; the matrices selected were Polypropylene (PP), Ethyl Vinyl<br />

NanoSafetyCluster - Compendium 2012<br />

Acetate (EVA) <strong>and</strong> Polyamide 6 (PA6). Three polymeric matrices<br />

with different polarities were chosen to amplify the range <strong>of</strong><br />

application <strong>of</strong> the polymeric nanocomposites. The nanomaterials<br />

obtained from WP1 were then incorporated into the polymeric<br />

matrices by extrusion processes <strong>and</strong> subsequently injected to<br />

obtain the polymeric nanocomposite demonstrators. The<br />

compatibilization <strong>and</strong> dispersibility <strong>of</strong> the nanomaterials in the<br />

polymeric matrices were evaluated by microscopy analysis (SEM).<br />

ICP-MS <strong>and</strong> TGA analysis were used to determine the<br />

concentration <strong>of</strong> nanomaterial in the polymeric matrices after each<br />

step <strong>of</strong> processing (extrusion <strong>and</strong> injection). Furthermore, physical<br />

characterization <strong>of</strong> the polymer nanocomposite demonstrators<br />

was focused on mechanical properties <strong>and</strong> thermal resistance<br />

determination (DMA, Dynamometric tests, HDT <strong>and</strong> VICAT, DSC).<br />

The results obtained showed that some polymers nanocomposites<br />

presented improved properties. However, further characterization<br />

analyses are in progress in order to establish relationships between<br />

dispersibility <strong>of</strong> the nanomaterials in the polymeric matrices <strong>and</strong><br />

the physical properties obtained.<br />

Nanocomposites<br />

PA6- 3% MWCNT<br />

Compendium <strong>of</strong> Projects in the European NanoSafety Cluster 163<br />

MWCNT<br />

+<br />

PA6<br />

Extrusion<br />

3.3 Weathering <strong>of</strong> polymer nanocomposites<br />

Injection<br />

The climatic chambers were tailored for the weathering tests to be<br />

done within the Nanopolytox project. The demonstrators<br />

developed in WP2 <strong>and</strong> the raw nanomaterials, including<br />

unmodified polymers were (<strong>and</strong> still are being) submitted to the<br />

selected aging conditions <strong>and</strong> the potential releases <strong>of</strong><br />

nanomaterials from the polymeric matrices during ageing<br />

processes are collected <strong>and</strong> quantified.<br />

Therefore, raw nanomaterials <strong>and</strong> nanocomposites were (<strong>and</strong> are<br />

being) exposed to an accelerated aging in weathering chambers<br />

for 1000h <strong>and</strong> combining climate <strong>and</strong> sunlight radiation, under the<br />

modified normative ISO 4892-2. The nanomaterials released from<br />

the polymeric matrices during ageing are extracted from the<br />

collected water by freeze-drying (lyophilisation) <strong>and</strong> then<br />

quantified by ICPMS <strong>and</strong> further analyzed by other analytical<br />

techniques (BET, FTIR, TGA, ICP-MS, DSC) to determine their<br />

physico-chemical properties.<br />

Aged nanomaterials in the powder form after being submitted to<br />

the whole process <strong>of</strong> ageing were dried <strong>and</strong> analyzed. After aging,<br />

all the nanomaterials except for nanoclays showed alterations<br />

compare to the corresponding non-aged nanomaterial. The main<br />

difference is the hydration <strong>of</strong> all the nanomaterials. Furthermore,<br />

in some cases, FT-IR indicates the modification <strong>of</strong> nanomaterial<br />

surface chemistry. FT-IR results were supported by the results<br />

obtained by BET analyses showing, for those nanomaterials with<br />

modified surface chemistries, a significant change in the surface<br />

area, pore volume <strong>and</strong>/or pore diameter <strong>of</strong> the material. For<br />

functionalized nanomaterials, a gain in surface area values<br />

indicates a loss <strong>of</strong> functional groups on the surface <strong>of</strong> the<br />

nanomaterial or a decrease in particle size. However, further

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