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Challenges of Regulation and Risk Assessment of Nanomaterials

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Although the ISO framework for LCA is not specific for nanomaterials, it can be adapted to them. The<br />

main problem with LCA <strong>of</strong> nanomaterials <strong>and</strong> nanoproducts is the lack <strong>of</strong> data <strong>and</strong> underst<strong>and</strong>ing in<br />

certain areas. Major efforts are needed to fully assess potential risks <strong>and</strong> environmental impacts <strong>of</strong><br />

nanoproducts <strong>and</strong> materials (not just those related to LCA). There is a need for protocols <strong>and</strong><br />

practical methodologies for toxicology studies, fate <strong>and</strong> transport studies <strong>and</strong> scaling approaches.<br />

Further research is needed to gather missing relevant data <strong>and</strong> to develop user-friendly eco-design<br />

screening tools.<br />

Nanopolytox will address the following issues for nanomaterials over their life cycle: physical <strong>and</strong><br />

chemical characterization at the different stages; hazard characterization (human toxicity <strong>and</strong><br />

ecotoxicity) at the different stages; transformation, migration <strong>and</strong> release <strong>of</strong> nanomaterials included<br />

in products; environmental <strong>and</strong> biological fate <strong>of</strong> released nanomaterials; LCA analysis <strong>of</strong><br />

nanomaterials included in polymeric products; technological solutions for recycling <strong>and</strong> final<br />

treatment <strong>of</strong> polymer nanocomposites. S. Vázquez Campos, summarised the Nanopolytox workplan<br />

<strong>and</strong> timelines as well as its methodological aspects. The project will finalise in 2013.<br />

The presentation on Health, Safety, <strong>and</strong> Environment: <strong>Assessment</strong> Methods was made by D.<br />

Hristozov, including the comprehensive weight <strong>of</strong> evidence approach adopted within the ENPRA<br />

project. According to him, substantial limitations <strong>and</strong> uncertainties hinder the risk assessment (RA)<br />

<strong>and</strong> the lifecycle assessment (LCA) <strong>of</strong> engineered nanomaterials (ENMs), thus making difficult the<br />

implementation <strong>of</strong> appropriate risk management measures.<br />

Limitations <strong>of</strong> conventional RA lie mainly in the fields <strong>of</strong> hazard identification, dose-response<br />

relationship assessment <strong>and</strong> exposure assessment. Accordingly, there is an Increasing interest in<br />

development <strong>of</strong> complementary methodologies methodologies/models (as the XL<br />

Insurance Database Methodology, the precautionary matrix for synthetic nanomaterials, the ANSES<br />

System, the St<strong>of</strong>fenmanager Nano 1.0 <strong>and</strong> the NANOSAFER) <strong>and</strong> tools (weight <strong>of</strong> evidence (WoE),<br />

multi criteria decision analysis (MCDA), control b<strong>and</strong>ing, expert elicitation (EE)) for RA <strong>of</strong> ENMs. After<br />

making a review <strong>of</strong> them, the presenter concluded that none <strong>of</strong> the methodologies/models are<br />

intended to facilitate regulatory decision making, but instead mostly to serve as preliminary risk<br />

screening tools for use by SMEs <strong>and</strong> industry. There is indeed a need for quantitative risk assessment<br />

approach supporting near-term regulatory decisions.<br />

On the other side, although LCA is usually applied to matured technologies, there is a general trend<br />

toward an earlier adoption <strong>of</strong> LCA, indeed LCA <strong>of</strong> nanotechnology <strong>and</strong> nanoproducts can provide an<br />

opportunity for precautionary action in order to prevent or minimize potential impact to human<br />

health <strong>and</strong> the environment <strong>and</strong> can add supplementary environmental information to support<br />

decisions on the regulation <strong>of</strong> certain nanomaterials or nanoproducts. However few LCA studies on<br />

nanotechnologies have been published <strong>and</strong> whereas the ISO 14040 framework is appropriate, a<br />

number <strong>of</strong> issues need to be addressed as the lack <strong>of</strong> inventory data: (i.e. data about nanomaterial<br />

releases during manufacturing, use <strong>and</strong> disposal stages are not available) <strong>and</strong> how to correlate the<br />

nanomaterials releases with the characterization factors/ environmental indicators used within the<br />

LCA framework.<br />

Actually RA <strong>and</strong> LCA procedures are complementary. Indeed, although LCA is readily applicable to<br />

nanoproducts, the methodology faces limitations when addressing the toxicity <strong>of</strong> ENMs released<br />

throughout their life cycle, which is a strength <strong>of</strong> the RA. Both LCA <strong>and</strong> risk assessment are costly<br />

exercises, integration <strong>of</strong> RA <strong>and</strong> LCA (i.e. a pragmatic screening approach combining the use <strong>of</strong> LCA,<br />

risk assessment <strong>and</strong> scenario analysis) holds promise to support a more holistic nanotechnological<br />

assessment that will allow better underst<strong>and</strong>ing <strong>of</strong> the environmental <strong>and</strong> health impacts <strong>and</strong> the<br />

economic <strong>and</strong> social benefits <strong>of</strong> the nanoproducts. Clearly understood <strong>and</strong> communicated benefits<br />

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