Are nanoplastics able to bind significant amount of metals? The lead example. (June 2019)

• Record Type: Journal Article
• Authors: Davranche, Mélanie; Veclin, Cloé; Pierson-Wickmann, Anne-Catherine; El Hadri, Hind; Grassl, Bruno; Rowenczyk, Laura; Dia, Aline; Ter Halle, Alexandra; Blancho, Florent; Reynaud, Stephanie; Gigault, Julien
• Is Part Of: Environmental pollution. Volume 249(2019)
• Page Start: 940
• Page End: 948
• Publication Date: 2019-06
• Subjects: Nanoplastics -- Pb(II) -- Adsorption -- Kinetics -- DLS -- A4F; Pollution -- Periodicals; Pollution -- Environmental aspects -- Periodicals; Environmental Pollution -- Periodicals; Pollution -- Périodiques; Pollution -- Aspect de l'environnement -- Périodiques; Pollution -- Effets physiologiques -- Périodiques; Pollution; Pollution -- Environmental aspects; Periodicals; Electronic journals; 363.73
• DOI: 10.1016/j.envpol.2019.03.087
• Languages: English
• ISSNs: 0269-7491

Abstract

Abstract: The nanoscale size of plastic debris makes them potential efficient vectors of many pollutants and more especially of metals. In order to evaluate this ability, nanoplastics were produced from microplastics collected on a beach exposed to the North Atlantic Gyre. The nanoplastics were characterized using multi-dimensional methods: asymmetrical flow field flow fractionation and dynamic light scattering coupled to several detectors. Lead (II) adsorption kinetics, isotherm and pH-edge were then carried out. The sorption reached a steady state after around 200 min. The maximum sorption capacity varied between 97% and 78.5% for both tested Pb concentrations. Lead (II) adsorption kinetics is controlled by chemical reactions with the nanoplastics surface and to a lesser extent by intraparticle diffusion. Adsorption isotherm modeling using Freundlich model demonstrated that NPG are strong adsorbents equivalent to hydrous ferric oxides such as ferrihydrite (log K a d s f r e u n d l i c h = 8.36 against 11.76 for NPG and ferrihydrite, respectively). The adsorption is dependent upon pH, in response to the Pb(II) adsorption by the oxygenated binding sites developed on account of the surface UV oxidation under environmental conditions. They could be able to compete with Fe or humic colloids for Pb binding regards to their amount and specific areas. Nanoplastics could therefore be efficient vectors of Pb and probably of many other metals as well in the environment. Graphical abstract: Image 1 Highlights: Pb(II) binding experiments onto nanoplastics extracted from environmental micro-plastics were performed. Pb(II) was largely bound onto nanoplastics by specific adsorption and intraparticle diffusion. Nanoplastics could be significant vectors of metals in the environment.