2017
DOI: 10.1039/c7en00251c
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Modeling human health characterization factors for indoor nanomaterial emissions in life cycle assessment: a case-study of titanium dioxide

Abstract: A dynamic life cycle impact assessment model demonstrates a non-constant intake fraction of inhaled nano-TiO2 as total emissions changes.

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Cited by 10 publications
(9 citation statements)
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“…The relevant determinants considered were energy and duration of the process/activity, volume of the facility (personal area, room, industrial facility or surrounding area), dustiness (very high (extremely fine and light powder), high (fine powder), medium (coarse powder), low and very low (extremely coarse powder)), solubility, weight fraction (% purity), moisture level, viscosity, and amount used. The NanoSerpa model was developed based on Michael P. Tsang [ 36 ] and Ganser et al [ 37 ] and adapted to require the minimum user input as possible, as this was one of the biggest concerns for developing the app.…”
Section: Methodsmentioning
confidence: 99%
“…The relevant determinants considered were energy and duration of the process/activity, volume of the facility (personal area, room, industrial facility or surrounding area), dustiness (very high (extremely fine and light powder), high (fine powder), medium (coarse powder), low and very low (extremely coarse powder)), solubility, weight fraction (% purity), moisture level, viscosity, and amount used. The NanoSerpa model was developed based on Michael P. Tsang [ 36 ] and Ganser et al [ 37 ] and adapted to require the minimum user input as possible, as this was one of the biggest concerns for developing the app.…”
Section: Methodsmentioning
confidence: 99%
“…However, the ReCiPe toxicological impact categories were removed and replaced with those from USEtox v2.0. , This was done to address a particular hazard of interest regarding the human health impacts associated with ENM emissions in occupational indoor settings. While current life-cycle impact assessment (LCIA) methods do not currently incorporate nanospecific characterization factors (CF), there have been a couple of such CF published recently. The CF from Tsang et al was applied in order to estimate the potential impacts from emissions that occur during transferring and handling these particles in postproduction scenarios …”
Section: Methodsmentioning
confidence: 99%
“…30−32 The CF from Tsang et al was applied in order to estimate the potential impacts from emissions that occur during transferring and handling these particles in postproduction scenarios. 32 Cumulative energy demands were calculated using the approach from Hischier et al 33 Primary inventory data for the SFFS were collected inhouse at the ICMCB and ISM, while additional foreground data were modeled using stoichiometric calculations based on technical documentation available in the literature. 34 Background (i.e., secondary) inventory data were taken from the Ecoinvent v3.2 allocation database (The Ecoinvent Association, Zurich) with all primary and foreground energy and transportation modeled using average European mixes.…”
Section: ■ Introductionmentioning
confidence: 99%
“…The behaviour of engineered nanomaterials in indoor environments is concentration dependent and driven by dynamic mechanisms that existing steady-state LCIA models fail to describe. To evaluate the human health hazards posed by engineered nanomaterials at the manufacturing phase, Tsang et al (2017) have developed a dynamic model as well as exposure scenarios to model different situations of nanomaterial handling in a workplace. To go one step further, these LCIA exposure models could be refined according to users' archetypes based on behaviour-related aspects (working time, preventive measures in the production phase) generated by an ABM.…”
Section: Recent Lca Developments For Which Abm Could Be Relevantmentioning
confidence: 99%