Mobilisation of antimony from microplastics added to coastal sediment

Antimony (Sb) widely occurs in plastics as a pigment and reaction residue and through the use and recycling of electronic material enriched in Sb as a flame retardant synergist. In this study, clean estuarine sediment has been contaminated by different microplastics prepared from pre-characterised s...

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Bibliographic Details
Published inEnvironmental pollution (1987) Vol. 264; p. 114696
Main Authors James, Elanor, Turner, Andrew
Format Journal Article
LanguageEnglish
Published England Elsevier Ltd 01.09.2020
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Summary:Antimony (Sb) widely occurs in plastics as a pigment and reaction residue and through the use and recycling of electronic material enriched in Sb as a flame retardant synergist. In this study, clean estuarine sediment has been contaminated by different microplastics prepared from pre-characterised samples of different types of plastic (including a rubber) containing a range of Sb concentrations (256–47,600 μg g−1). Sediment-plastic mixtures in a mass ratio of 100:1 were subject to 6-h extractions in seawater and in seawater solutions of a protein (bovine serum albumin; BSA) and a surfactant (taurocholic acid; TA) that mimic the digestive conditions of coastal deposit-feeding invertebrates. Most time-courses for Sb mobilisation could be defined by a second-order diffusion equation, with rate constants ranging from 44.6 to 0.0216 (μg g−1)−1 min−1. Bioaccessibilities, defined as maximum extractable concentrations throughout each time course relative to total Sb content, ranged from <0.01% for a polycarbonate impregnated with Sb as a synergist exposed to all solutions, to >1% for acrylonitrile butadiene styrene containing a Sb-based colour pigment exposed to solutions of BSA and TA and recycled industrial polyethylene exposed to BSA solution. The potential for Sb to bioaccumulate or elicit a toxic effect is unknown but it is predicted that communities of deposit-feeders could mobilise significant quantities of Sb in sediment contaminated by microplastics through bioturbation and digestion. [Display omitted] •Plastics containing antimony were micronized and added to estuarine sediment.•The mobility of Sb was studied in seawater and solutions of a protein and a surfactant.•Mobilisation kinetics usually conformed to a second-order diffusion model.•Mobilisation ranged from <0.1% to >1% depending on the plastic and solution.•Sb could be mobilised via digestion and bioturbation of sediment by deposit-feeders. Antimony is mobilised from plastics added to sediment by seawater and solutions of a protein and a surfactant via a diffusion model.
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ISSN:0269-7491
1873-6424
1873-6424
DOI:10.1016/j.envpol.2020.114696