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Ionic liquids, clay content, organic matter, mixture toxicity, phytotoxicity, kaolinite, smectite, testbattery, hazard assessment, soils. - This study contributes to a prospective hazard assessment of ionic liquids (ILs) for the terrestrial environment by analysing the (bio)availability (and therefore toxicity) of selected imidazolium based ILs in dependence on the soil properties organic matter, clay type and clay content. In general this hazard assessment is complicated by the structural heterogeneity within the substance class of ionic liquids which provides an almost unlimited number of theoretically available chemical structures. For this reason a tiered testing strategy was used to efficiently analyse the hazard potential of selected ILs starting with theoretical assumptions according to the T-SAR (Thinking in Terms of Structure Activity Relationships) concept followed by a set up of different test kits. Those assumptions were experimentally validated with an (eco)toxicological test battery and followed by a closer analysis of the (bio)availability of selected ILs. The bioavailability was assessed by using sorption/desorption studies as well as phytotoxicity assays. Additionally the issue of mixture toxicity was analysed for ILs mixtures in the presences and absence of the heavy metal cadmium.
In: Environmental science and pollution research: ESPR, Band 23, Heft 5, S. 4120-4128
ISSN: 1614-7499
In: Environmental science and pollution research: ESPR, Band 23, Heft 5, S. 4218-4234
ISSN: 1614-7499
A substance may have one or more nanoforms, defined for regulatory purposes under EU chemicals legislation REACH based on differences in physicochemical properties such as size, shape, specific surface area and surface chemistry including coatings. To reduce the burden of testing each unique nanoform for the environmental risk assessment of nanomaterials, grouping approaches allow simultaneous assessment of multiple nanoforms. Nanoforms with initially different intrinsic properties, could still be considered similar if their environmental fate and effects can be demonstrated to be similar. One hypothesis to group nanoforms with different organic surface modifications is to use parameters linked to biodegradation of the organic surface. The hypothesis contends that nanoforms with a similar core chemistry, but different organic surface treatments may be grouped, if the surface treatment is likely to be lost through biodegradation rapidly upon entering an environmental compartment, such that it no longer modulates fate, exposure and toxicity of the nanoform. To implement grouping according to surface treatment biodegradability, a robust approach to measure the breakdown of particle surface treatments is needed. We present a tiered testing strategy to assess the biodegradation of organic surface treatments used with nanomaterials that can be implemented as part of an Integrated Approach to Testing and Assessment (IATA) for grouping based on surface treatment stability. The tiered approach consists of an initial pre-screening MT2 colorimetric carbon substrate utilisation assay, to provide a rapid assessment of coating degradation, and a second tier of testing using OECD Test Guideline 301F for assessing organic chemical biodegradability. Six common surface treatment substances are assessed using the tiered testing strategy to refine rules for escalating between tiers. Similarity assessment using absolute Euclidean distances and x-fold difference concluded that the Tier 1 assessment can be used as conservative binary ...
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Nanomaterial risk governance requires models to estimate the material flow, fate and transport as well as uptake/bioavailability, hazard and risk in the environment. This study assesses the fit of such available models to different stages during the innovation of nano-enabled products. Through stakeholder consultations, criteria were identified for each innovation stage from idea conception to market launch and monitoring. In total, 38 models were scored against 41 criteria concerning model features, applicability, resource demands and outcome parameters. A scoring scheme was developed to determine how the models fit the criteria of each innovation stage. For each model, the individual criteria scores were added, yielding an overall fit score to each innovation stage. Three criteria were critical to stakeholders and incorporated as multipliers in the scoring scheme; the required time/costs and level of expertise needed to use the model, and for risk assessment models only, the option to compare PEC and PNEC. Regulatory compliance was also identified as critical, but could not be incorporated, as a nanomaterial risk assessment framework has yet to be developed and adopted by legislators. In conclusion, the scoring approach underlined similar scoring profiles across stages within model categories. As most models are research tools designed for use by experts, their score generally increased for later stages where most resources and expertise are committed. In contrast, stakeholders need relatively simple models to identify potential hazards and risk management measures at early product development stages to ensure safe use of nanomaterials without costs and resource needs hindering innovation. ; acceptedVersion ; Peer reviewed
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In: Sørensen , S N , Baun , A , Burkard , M , Dal Maso , M , Hansen , S F , Harrison , S , Hjorth , R , Lofts , S , Matzke , M , Nowack , B , Peijnenburg , W , Poikkimäki , M , Quik , J T K , Schirmer , K , Verschoor , A , Wigger , H & Spurgeon , D J 2019 , ' Evaluating environmental risk assessment models for nanomaterials according to requirements along the product innovation Stage-Gate process ' , Environmental Science: Nano , vol. 6 , no. 2 , pp. 505-518 . https://doi.org/10.1039/C8EN00933C
Nanomaterial risk governance requires models to estimate the material flow, fate and transport as well as uptake/bioavailability, hazard and risk in the environment. This study assesses the fit of such available models to different stages during the innovation of nano-enabled products. Through stakeholder consultations, criteria were identified for each innovation stage from idea conception to market launch and monitoring. In total, 38 models were scored against 41 criteria concerning model features, applicability, resource demands and outcome parameters. A scoring scheme was developed to determine how the models fit the criteria of each innovation stage. For each model, the individual criteria scores were added, yielding an overall fit score to each innovation stage. Three criteria were critical to stakeholders and incorporated as multipliers in the scoring scheme; the required time/costs and level of expertise needed to use the model, and for risk assessment models only, the option to compare PEC and PNEC. Regulatory compliance was also identified as critical, but could not be incorporated, as a nanomaterial risk assessment framework has yet to be developed and adopted by legislators. In conclusion, the scoring approach underlined similar scoring profiles across stages within model categories. As most models are research tools designed for use by experts, their score generally increased for later stages where most resources and expertise are committed. In contrast, stakeholders need relatively simple models to identify potential hazards and risk management measures at early product development stages to ensure safe use of nanomaterials without costs and resource needs hindering innovation.
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