“…Based on the current knowledge, more research works are expected on the engineering of degradable and less toxic NPs to minimize their environment related issues. For example, due to the fact that organic solvents can alter the shape, size, and other physicochemical properties of NPs that ultimately modulate biological, chemical, and environmental properties (Ali et al, 2017), the toxicity and bioavailability of MeO-NPs can be tailored by modifying the synthesis parameters/conditions (Ali et al, 2017;Caramazana-Gonz alez et al, 2017;Papadaki et al, 2017;Punnoose et al, 2014) or by coating with biologically inert compounds (Ortelli et al, 2016;Sotiriou et al, 2014). Punnoose et al (2014) synthesized two ZnO-NP samples (size, 9.26 nm each) from the same precursor, zinc acetate, and modified their surface chemical structures using different reaction solvents, diethylene glycol and denatured ethanol, which led to major differences in the z-potential, R D , photocatalytic rate constant, and more importantly, their cytotoxic effects on Hut-78 cancer cells (IC 50 , 0.37 and 0.56 mM, using diethylene glycol and denatured ethanol reaction solvents, respectively).…”
Section: Future Research Directionsmentioning
confidence: 99%
“…Besides, coated ZnO-NPs and TiO 2 -NPs (Ortelli et al, 2016) exhibited lower toxic-effects due to minimum dissolution and no direct contact with cellular bodies in the case of ZnO-NPs and avoid the ROS generation for the case of TiO 2 -NPs. In the report of Papadaki et al (2017), a ZnO-NPs synthesis route based on electricity and renewable energy can improve the environmental sustainability of the nanoparticles by 25%. Besides, a precursor selection in preparation of NPs also plays a great role in determining cradle-to-gate environmental impacts.…”
“…Based on the current knowledge, more research works are expected on the engineering of degradable and less toxic NPs to minimize their environment related issues. For example, due to the fact that organic solvents can alter the shape, size, and other physicochemical properties of NPs that ultimately modulate biological, chemical, and environmental properties (Ali et al, 2017), the toxicity and bioavailability of MeO-NPs can be tailored by modifying the synthesis parameters/conditions (Ali et al, 2017;Caramazana-Gonz alez et al, 2017;Papadaki et al, 2017;Punnoose et al, 2014) or by coating with biologically inert compounds (Ortelli et al, 2016;Sotiriou et al, 2014). Punnoose et al (2014) synthesized two ZnO-NP samples (size, 9.26 nm each) from the same precursor, zinc acetate, and modified their surface chemical structures using different reaction solvents, diethylene glycol and denatured ethanol, which led to major differences in the z-potential, R D , photocatalytic rate constant, and more importantly, their cytotoxic effects on Hut-78 cancer cells (IC 50 , 0.37 and 0.56 mM, using diethylene glycol and denatured ethanol reaction solvents, respectively).…”
Section: Future Research Directionsmentioning
confidence: 99%
“…Besides, coated ZnO-NPs and TiO 2 -NPs (Ortelli et al, 2016) exhibited lower toxic-effects due to minimum dissolution and no direct contact with cellular bodies in the case of ZnO-NPs and avoid the ROS generation for the case of TiO 2 -NPs. In the report of Papadaki et al (2017), a ZnO-NPs synthesis route based on electricity and renewable energy can improve the environmental sustainability of the nanoparticles by 25%. Besides, a precursor selection in preparation of NPs also plays a great role in determining cradle-to-gate environmental impacts.…”
“…Figure 2(a) shows the optical properties of ZnO nanoparticles synthesized at 2 minutes of irradiation time. A sharp peak was formed at 355 nm, representing the hexagonal phase of ZnO nanoparticle [27].…”
“…In our case, it is important to assess whether the combination of films with ZnO NP does not generate an impact that surpasses that avoided by the waste savings. The environmental burden of ZnO NP production has been previously evaluated in the field of material engineering [20] and chemical functionality [21], but never when it comes to its inclusion in films for the manufacturing of active films. In [21], the authors claim that one of the main environmental weaknesses of ZnO NP production is electricity consumption.…”
Section: Introductionmentioning
confidence: 99%
“…The environmental burden of ZnO NP production has been previously evaluated in the field of material engineering [20] and chemical functionality [21], but never when it comes to its inclusion in films for the manufacturing of active films. In [21], the authors claim that one of the main environmental weaknesses of ZnO NP production is electricity consumption. Nevertheless, the small amounts of nanoparticles needed to produce novel packaging technologies may lead to a negligible effect of this issue.…”
In order to enlarge the shelf life and avoid the waste of fresh-cut (FC) products, novel packaging techniques with antimicrobial properties have been proposed. In this work, we analyzed the potential environmental benefits of using films reinforced with bactericidal ZnO nanoparticles (NP) for FC produce packaging, when compared to the traditional polypropylene (PP) films. A biodegradable, polylactic acid (PLA) package and a non-biodegradable, polypropylene package, both coated with ZnO NP, were considered as novel technologies. The eco-profile of the considered alternatives was assessed via two life cycle assessments (LCAs). Firstly, an attributional LCA was performed in order to compare the materials in terms of their production and end of life (EOL) processes, allowing us to extend the conclusions to different food products. Secondly, a consequential LCA was performed taking into account the whole life cycle of the fresh vegetable, with special attention to the environmental implications of the produce losses among the chain. The uncertainties of the models were assessed via Monte Carlo approach. In both cases, the scenarios concerning the PLA and PP active packages with ZnO NP showed a better profile than the traditional techniques, specifically when considering the full supply chain of the FC vegetables in the consequential LCA. As agricultural production is the main contributor to the environmental impact of the cycle, the avoidance of wastes by extending the shelf life through the novel packages leads to the impact reduction of FC products.
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