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Review
. 2021 Jul 27:12:100110.
doi: 10.1016/j.wroa.2021.100110. eCollection 2021 Aug 1.

Paint particles in the marine environment: An overlooked component of microplastics

Affiliations
Review

Paint particles in the marine environment: An overlooked component of microplastics

Andrew Turner. Water Res X. .

Abstract

Because paint particles consist of a resin (polymer) combined with one or more additives, they bear compositional similarities with microplastics. Despite these shared characteristics, however, paint particles are often undetected, deliberately overlooked or evade classification in the pool of micro-debris (all synthetic debris of < 5 mm in size), and in particular in the marine setting where an extensive body of microplastic literature exists. Accordingly, the present paper provides a critical insight into the physico-chemical properties, sources, distributions, behaviour and toxicity of paint particles in the marine environment. Paint particles contain a greater proportion of additives than plastics and, consequently, are more brittle, angular, opaque, dense, heterogeneous and layered than microplastics of equivalent dimensions. Land-based sources of paint particles, including deteriorating or disturbed coatings on roads and building, are transported to the ocean with other microplastics via urban runoff, water treatment facilities and the atmosphere. However, inputs of paint particles are enhanced significantly and more directly by the disturbance, erosion and weathering of coatings on coastal structures, boats and ships. Estimates of paint particle emissions to the marine environment vary widely, with calculated contributions to the total synthetic micro-debris input as high as 35%. Upper estimates are consistent with available (albeit limited) quantitative information on the relative abundance of paint particles amongst synthetic material captured by sea surface trawls and ingested by marine animals. Of greatest environmental concern is the high chemical toxicity of paint particles compared with similarly-sized microplastics and other synthetic debris. This results from the contemporary and historical use of high concentrations of hazardous inorganic additives in marine antifouling and land-based paints, and the relatively ready mobilisation of harmful ions, like Cu+/Cu2+, TBT+, Pb2+ and CrO4 2-, from the matrix. Recommendations arising from this review include greater use of particulate capturing devices, waste collection systems and recycling facilities during paint disturbance, raising awareness of the potential impacts of discarded paint amongst users, and alerting the microplastic community to the significance of paint particles and developing means by which they are isolated from environmental samples.

Keywords: Composition; Impacts; Marine environment; Microplastics; Paint particles; Toxicity.

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Conflict of interest statement

The author declares that he has no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.

Figures

Fig 1
Fig. 1
The chemical constituents of plastics and paints. Polymers, pigments, fillers and certain additives are common to both materials (with the arrow showing the direction of greater abundance) while other additives are more specific to either general or speciality plastics or paints.
Fig 2
Fig. 2
Sources of paint particles (from different users and applications) to the marine environment.
Fig 3
Fig. 3
Images illustrating some of the specific sources of paint particles to the marine environment. (a) Painted wooden boards that had been dumped on a beach, (b) paint peeling off a road bridge, (c) paint deteriorating from the hull and rails of an abandoned ship, (d) crumbling yellow road paint, (e) a painted, beached fishing float, (f) the hull of a boat having recently been power-sanded, and (g) a fragment of painted plastic retrieved from a beach near a coastal landfill site. (Images courtesy of Andrew Turner, Madeleine Lewis and Christina Muller-Karanassos).
Fig 4
Fig. 4
Density ranges of common plastics (LDPE = low density polyethylene; HDPE = high density polyethylene; PP = polypropylene; ABS = acrylonitrile butadiene styrene; PET = polyethylene terephthalate; PVC = polyvinyl chloride) and dried paint formulations. Annotated are the density ranges of seawater and solutions of ZnCl2 commonly employed to isolate microplastics from sediment. Sources of information: Powell and Zinn (1983); Ruble (2002); Brockenbrough (2009); Cobb (2009); Fontana and Grass (2010); PPG Aerospace (2014); Soroldoni et al. (2018); SpecialChem (2021); Zhejiang Brother Guidepost Paint (2021).
Fig 5
Fig. 5
X-ray fluorescent spectra, with selected peaks identified, acquired over the range 0 to 14 keV using a Niton XL3t GOLDD+ for (a) an antifouling paint fragment and (b) a pigmented, beached plastic. Elemental concentrations, where quantified, are annotated in mg kg−1 along with the percentage balance (comprising of light elements not detected by the instrument). (Author's unpublished data.)
Fig 6
Fig. 6
Sources, transport and impacts of paint particles in the marine environment. The metal ions shown in the box are those of greatest ecotoxicological concern that are mobilised from paint.

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